chemical safety report sections 9 & 10 chesar cobalt...
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Cobalt dinitrate
CHEMICAL SAFETY REPORT
SECTIONS 9 & 10
CHESAR
Cobalt dinitrate
Draft Report
18 October 2019
Revised version of 29 November 2019
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Table of Contents
9. EXPOSURE ASSESSMENT (and related risk characterisation) ................................................... 10 9.0. Introduction ............................................................................................................................... 10 9.0.1. Overview on uses .................................................................................................................. 10 9.0.2. Assessment entity groups ...................................................................................................... 10 9.0.3. Introduction to the assessment for the environment ................................................................ 10 9.0.4. Introduction to the assessment for workers ............................................................................ 13 9.0.5. Introduction to the assessment for consumers ........................................................................ 14 9.1. Exposure scenario 1: Manufacture - Manufacture of cobalt dinitrate .......................................... 15 9.1.1. Env CS 1: Manufacture of cobalt dinitrate ES1 STP Discharge (ERC 1) ................................. 15 9.1.2. Env CS 2: Manufacture of cobalt dinitrate ES2 Direct Discharge (ERC 1) ............................... 17 9.1.3. Env CS 3: Manufacture of cobalt dinitrate ES3 Marine Discharge (ERC 1) ............................. 19 9.1.4. Worker CS 4: Raw material handling (PROC 26, PROC 21; PROC 8b) .................................. 21 9.1.5. Worker CS 5: Preparation of raw material (PROC 3, PROC 1) ............................................... 23 9.1.6. Worker CS 6: Wet process (PROC 4, PROC 1) ...................................................................... 25 9.1.7. Worker CS 7: Hot process (PROC 22, PROC 1; PROC 27a) .................................................. 27 9.1.8. Worker CS 8: Further processing (PROC 5, PROC 1) ............................................................ 28 9.1.9. Worker CS 9: Filling of liquids in closed system (PROC 2)...................................................... 30 9.1.10. Worker CS 10: Filling of solutions (PROC 8b)....................................................................... 32 9.1.11. Worker CS 11: Handling of powders with moderate dustiness potential (PROC 26) .............. 34 9.1.12. Worker CS 12: Handling of powders with high dustiness potential (PROC 26) ...................... 35 9.1.13. Worker CS 13: Cleaning & Maintenance (PROC 28) ............................................................ 37 9.2. Exposure scenario 2: Manufacture - Manufacture of cobalt nitrate within catalyst or catalyst precursors ....................................................................................................................................... 40 9.2.1. Env CS 1: Manufacture of cobalt nitrate within catalyst or catalyst precursors ES1 STP Discharge (ERC 1) .......................................................................................................................... 40 9.2.2. Env CS 2: Manufacture of cobalt nitrate within catalyst or catalyst precursors ES2 Direct Discharge (ERC 1) .......................................................................................................................... 42 9.2.3. Env CS 3: Manufacture of cobalt nitrate within catalyst or catalyst precursors ES3 Marine Discharge (ERC 1) .......................................................................................................................... 44 9.2.4. Worker CS 4: M1 Dissolution of cobalt metal to form cobalt dinitrate (PROC 3, PROC 2; PROC 9) .................................................................................................................................................... 46 9.2.5. Worker CS 5: MNCM: Cleaning and maintenance (PROC 28) ................................................ 48 9.3. Exposure scenario 3: Use at industrial sites - Manufacture of cobalt carboxylates and resinates (intermediate use)............................................................................................................................ 51 9.3.1. Env CS 1: Manufacture of cobalt carboxylates and resinates (intermediate use) (ERC 6a) ..... 51 9.3.2. Worker CS 2: Raw material handling (PROC 26, PROC 8b) ................................................... 53 9.3.3. Worker CS 3: Reaction (PROC 4, PROC 1; PROC 3) ............................................................ 55 9.3.4. Worker CS 4: Cleaning & Maintenance (PROC 28) ................................................................ 57 9.4. Exposure scenario 4: Use at industrial sites - Manufacture of chemicals and in other wet-chemical processes as intermediate ............................................................................................................... 60 9.4.1. Env CS 1: Manufacture of chemicals and in other wet-chemical processes as intermediate ES1 STP Discharge (ERC 6a) ................................................................................................................. 60 9.4.2. Env CS 2: Manufacture of chemicals and in other wet-chemical processes as intermediate ES2 Direct Discharge (ERC 6a) .............................................................................................................. 62 9.4.3. Env CS 3: Manufacture of chemicals and in other wet-chemical processes as intermediate ES3 Marine Discharge (ERC 6a) ............................................................................................................. 64 9.4.4. Worker CS 4: Raw material handling (PROC 26, PROC 8b; PROC 9) .................................... 66
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9.4.5. Worker CS 5: Mixing/Reaction in vessel/bath (PROC 3, PROC 1; PROC 2; PROC 4; PROC 5)........................................................................................................................................................ 68 9.4.6. Worker CS 6: Cleaning & Maintenance (PROC 28) ................................................................ 70 9.5. Exposure scenario 5: Use at industrial sites - Industrial use of RM as intermediate for the production of another substance in catalyst or catalyst precursor manufacture ................................. 72 9.5.1. Env CS 1: Industrial use of RM as intermediate for the production of another substance in catalyst or catalyst precursor manufacture ES1 STP Discharge (ERC 6a) ........................................ 73 9.5.2. Env CS 2: Industrial use of RM as intermediate for the production of another substance in catalyst or catalyst precursor manufacture ES2 Direct Discharge (ERC 6a) ..................................... 75 9.5.3. Env CS 3: Industrial use of RM as intermediate for the production of another substance in catalyst or catalyst precursor manufacture ES3 Marine Discharge (ERC 6a) .................................... 77 9.5.4. Worker CS 4: N1: Delivery and storage of cobalt nitrate raw material (PROC 8b, PROC 3; PROC 4; PROC 9) ........................................................................................................................... 79 9.5.5. Worker CS 5: N2: Dissolution of cobalt nitrate raw material (PROC 3, PROC 9) ..................... 80 9.5.6. Worker CS 6: N3: Impregnation, drying & calcination of cobalt nitrate (PROC 4, PROC 1; PROC 2; PROC 3) ........................................................................................................................... 82 9.5.7. Worker CS 7: N4: Precipitation of cobalt carbonate from cobalt nitrate solution (PROC 3, PROC 9) .................................................................................................................................................... 84 9.5.8. Worker CS 8: NCM: Cleaning and maintenance (PROC 28) ................................................... 86 9.6. Exposure scenario 6: Formulation or re-packing - Formulation of metal surface treatment pre-formulations ..................................................................................................................................... 88 9.6.1. Env CS 1: Formulation of metal surface treatment pre-formulations ES1 STP Discharge (ERC 2) .................................................................................................................................................... 88 9.6.2. Env CS 2: Formulation of metal surface treatment pre-formulations ES2 Direct Discharge (ERC 2) .................................................................................................................................................... 90 9.6.3. Env CS 3: Formulation of metal surface treatment pre-formulations ES3 Marine Discharge (ERC 2) ........................................................................................................................................... 92 9.6.4. Worker CS 4: Raw material handling (PROC 26, PROC 8b) ................................................... 94 9.6.5. Worker CS 5: Formulation of solutions (PROC 3, PROC 2) .................................................... 96 9.6.6. Worker CS 6: Filling of solutions containing <25 % of cobalt dinitrate (PROC 8b) ................... 98 9.6.7. Worker CS 7: Cleaning & Maintenance (PROC 28) ................................................................ 99 9.7. Exposure scenario 7: Use at industrial sites - Passivation processes in surface treatment ....... 102 9.7.1. Env CS 1: Passivation processes in surface treatment ES1 STP Discharge (ERC 5) ............ 102 9.7.2. Env CS 2: Passivation processes in surface treatment ES2 Direct Discharge (ERC 5) ......... 104 9.7.3. Env CS 3: Passivation processes in surface treatment ES3 Marine Discharge (ERC 5) ........ 106 9.7.4. Worker CS 4: Raw material handling (solid input materials) (PROC 5, PROC 1; PROC 2; PROC 8b)................................................................................................................................................. 108 9.7.5. Worker CS 5: Raw material handling (exclusively aqueous solutions as input materials) (PROC 4, PROC 9) .................................................................................................................................... 110 9.7.6. Worker CS 6: Passivation (PROC 13) .................................................................................. 111 9.7.7. Worker CS 7: Finishing of passivated articles (PROC 21) ..................................................... 113 9.7.8. Worker CS 8: Cleaning & Maintenance (PROC 28) .............................................................. 115 9.8. Exposure scenario 8: Use at industrial sites - Passivation processes in surface treatment at large industrial sites with continuous processes ...................................................................................... 118 9.8.1. Env CS 1: Passivation processes in surface treatment at large industrial sites with continuous processes ES1 STP Discharge (ERC 5) ........................................................................................ 118 9.8.2. Env CS 2: Passivation processes in surface treatment at large industrial sites with continuous processes ES2 Direct Discharge (ERC 5) ...................................................................................... 120 9.8.3. Env CS 3: Passivation processes in surface treatment at large industrial sites with continuous processes ES3 Marine Discharge (ERC 5)..................................................................................... 122 9.8.4. Worker CS 4: Raw material handling (exclusively aqueous solutions as input materials) (PROC 4, PROC 9) .................................................................................................................................... 124 9.8.5. Worker CS 5: Passivation (PROC 2, PROC 13) ................................................................... 126 9.8.6. Worker CS 6: Finishing of passivated articles (PROC 21) ..................................................... 128
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9.9. Exposure scenario 9: Use at industrial sites - Plating processes in surface treatment .............. 130 9.9.1. Env CS 1: Plating processes in surface treatment ES1 STP Discharge (ERC 5) ................... 130 9.9.2. Env CS 2: Plating processes in surface treatment ES2 Direct Discharge (ERC 5) ................. 132 9.9.3. Env CS 3: Plating processes in surface treatment ES3 Marine Discharge (ERC 5) ............... 134 9.9.4. Worker CS 4: Raw material handling (solid input materials) (PROC 5, PROC 1; PROC 2; PROC 8b)................................................................................................................................................. 136 9.9.5. Worker CS 5: Raw material handling (exclusively aqueous solutions as input materials) (PROC 4, PROC 9) .................................................................................................................................... 138 9.9.6. Worker CS 6: Plating (PROC 13) ......................................................................................... 139 9.9.7. Worker CS 7: Manual brush plating (PROC 10) .................................................................... 141 9.9.8. Worker CS 8: Finishing of coated/plated articles (PROC 21) ................................................ 143 9.9.9. Worker CS 9: Cleaning & Maintenance (PROC 28) .............................................................. 145 9.10. Exposure scenario 10: Service life (worker at industrial site) - Industrial handling of surface treated articles (passivated/plated) ................................................................................................ 148 9.10.1. Env CS 1: Handling of surface treated articles (passivated/plated) (ERC 12a) .................... 148 9.10.2. Worker CS 2: Handling of articles (PROC 21)..................................................................... 149 9.11. Exposure scenario 11: Service life (professional worker) - Professional handling of surface treated articles (passivated/plated) ................................................................................................ 152 9.11.1. Env CS 1: Handling of surface treated articles (passivated/plated) (ERC 10a) .................... 152 9.11.2. Worker CS 2: Handling of articles (PROC 21)..................................................................... 153 9.12. Exposure scenario 12: Formulation or re-packing - Formulation for water treatment chemicals, oxygen scavengers, corrosion inhibitors......................................................................................... 156 9.12.1. Env CS 1: Formulation for water treatment chemicals, oxygen scavengers, corrosion inhibitors ES1 STP Discharge (ERC 2) ......................................................................................................... 156 9.12.2. Env CS 2: Formulation for water treatment chemicals, oxygen scavengers, corrosion inhibitors ES2 Direct Discharge (ERC 2) ....................................................................................................... 158 9.12.3. Env CS 3: Formulation for water treatment chemicals, oxygen scavengers, corrosion inhibitors ES3 Marine Discharge (ERC 2) ..................................................................................................... 160 9.12.4. Worker CS 4: Formulation (PROC 26, PROC 15; PROC 2; PROC 4; PROC 5; PROC 8b; PROC 9) ....................................................................................................................................... 162 9.12.5. Worker CS 5: Cleaning & Maintenance (PROC 28) ............................................................ 164 9.13. Exposure scenario 13: Use at industrial sites - Use of water treatment chemicals, oxygen scavengers, corrosion inhibitors ..................................................................................................... 167 9.13.1. Env CS 1: Use of water treatment chemicals, oxygen scavengers, corrosion inhibitors ES1 STP Discharge (ERC 6b) ............................................................................................................... 167 9.13.2. Env CS 2: Use of water treatment chemicals, oxygen scavengers, corrosion inhibitors ES2 Direct Discharge (ERC 6b) ............................................................................................................ 169 9.13.3. Env CS 3: Use of water treatment chemicals, oxygen scavengers, corrosion inhibitors ES3 Marine Discharge (ERC 6b) ........................................................................................................... 171 9.13.4. Worker CS 4: Use of formulation (PROC 8b, PROC 2) ....................................................... 173 9.14. Exposure scenario 14: Use at industrial sites - Battery production (intermediate use) ............ 176 9.14.1. Env CS 1: Battery production (intermediate use) ES1 Direct Discharge (ERC 5)................. 176 9.14.2. Env CS 2: Battery production (intermediate use) ES2 Marine Discharge (ERC 5) ............... 178 9.14.3. Worker CS 3: Raw material handling (PROC 26, PROC 3; PROC 4; PROC 8b) ................. 180 9.14.4. Worker CS 4: Mix preparation (PROC 5, PROC 3) ............................................................. 182 9.14.5. Worker CS 5: Further processing (PROC 13, PROC 3; PROC 4; PROC 5; PROC 6; PROC 9)...................................................................................................................................................... 184 9.14.6. Worker CS 6: Final processing and handling (PROC 14, PROC 21) ................................... 185 9.14.7. Worker CS 7: Cleaning & Maintenance (PROC 28) ............................................................ 186 9.15. Exposure scenario 15: Service life (worker at industrial site) - Service life of cobalt-containing industrial batteries in industrial settings .......................................................................................... 189 9.15.1. Env CS 1: Service life of cobalt-containing industrial batteries in industrial settings (ERC 12a)...................................................................................................................................................... 189 9.15.2. Worker CS 2: Handling of closed containers (PROC 21)..................................................... 190
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9.16. Exposure scenario 16: Service life (professional worker) - Service life of cobalt-containing portable batteries in professional settings ...................................................................................... 192 9.16.1. Env CS 1: Service life of cobalt-containing portable batteries in professional settings (ERC 10a) ............................................................................................................................................... 192 9.16.2. Worker CS 2: Handling of closed containers (PROC 21)..................................................... 193 9.17. Exposure scenario 17: Formulation or re-packing - Formulation of mixtures for use in biogas production ..................................................................................................................................... 195 9.17.1. Env CS 1: Formulation of mixtures for use in biogas production ES1 STP Discharge (ERC 2)...................................................................................................................................................... 195 9.17.2. Env CS 2: Formulation of mixtures for use in biogas production ES2 Direct Discharge (ERC 2)...................................................................................................................................................... 197 9.17.3. Env CS 3: Formulation of mixtures for use in biogas production ES3 Marine Discharge (ERC 2) .................................................................................................................................................. 199 9.17.4. Worker CS 4: Raw material handling (PROC 26) ................................................................ 201 9.17.5. Worker CS 5: Formulation of solutions (PROC 3) ............................................................... 203 9.17.6. Worker CS 6: Production of solid formulations (PROC 3).................................................... 205 9.17.7. Worker CS 7: Filling of solutions containing <1 % of cobalt dinitrate (PROC 8b) ................. 206 9.17.8. Worker CS 8: Packaging of solid formulations containing <1 % of cobalt dinitrate (PROC 26)...................................................................................................................................................... 208 9.17.9. Worker CS 9: Cleaning & Maintenance (PROC 28) ............................................................ 210 9.18. Exposure scenario 18: Use at industrial sites - Use in biogas production ............................... 213 9.18.1. Env CS 1: Use in biogas production ES1 STP Discharge (ERC 4) ...................................... 213 9.18.2. Env CS 2: Use in biogas production ES2 Direct Discharge (ERC 4) ................................... 215 9.18.3. Env CS 3: Use in biogas production ES3 Marine Discharge (ERC 4) .................................. 217 9.18.4. Worker CS 4: Dosing of solid material (PROC 26) .............................................................. 219 9.18.5. Worker CS 5: Dosing of liquid material (PROC 8b, PROC 9) .............................................. 221 9.19. Exposure scenario 19: Widespread use by professional workers - Professional use of formulations in biogas production ................................................................................................... 223 9.19.1. Env CS 1: Professional use of formulations in biogas production (ERC 8e) ........................ 223 9.19.2. Worker CS 2: Handling of sealed bags (PROC 8b) ............................................................. 224 9.20. Exposure scenario 20: Use at industrial sites - Use in fermentation processes, in biotech and scientific research and standard analysis ....................................................................................... 227 9.20.1. Env CS 1: Use in fermentation processes, in biotech and scientific research and standard analysis ES1 STP Discharge (ERC 4) ............................................................................................ 227 9.20.2. Env CS 2: Use in fermentation processes, in biotech and scientific research and standard analysis ES2 Direct Discharge (ERC 4) ......................................................................................... 229 9.20.3. Env CS 3: Use in fermentation processes, in biotech and scientific research and standard analysis ES3 Marine Discharge (ERC 4) ........................................................................................ 231 9.20.4. Worker CS 4: Raw material handling (PROC 9, PROC 26; PROC 8b) ................................ 233 9.20.5. Worker CS 5: Operations in closed systems (PROC 3, PROC 1; PROC 2) ......................... 235 9.20.6. Worker CS 6: Handling at laboratory scale (PROC 15) ....................................................... 237 9.20.7. Worker CS 7: Handling of liquid stock solution (PROC 5, PROC 3; PROC 8b; PROC 9) ..... 239 10. RISK CHARACTERISATION RELATED TO COMBINED EXPOSURE .................................... 241 10.1. Human health ....................................................................................................................... 241 10.1.1. Workers ............................................................................................................................. 241 10.1.2. Consumer .......................................................................................................................... 242 10.2. Environment (combined for all emission sources) .................................................................. 242 10.2.1. All uses (regional scale) ..................................................................................................... 242 10.2.2. Regional assessment ......................................................................................................... 243
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List of Tables
Table 9.1. Tonnage for assessment ................................................................................................. 10 Table 9.2. Type of risk characterisation required for the environment ............................................... 10 Table 9.3. Substance key phys-chem and fate properties................................................................. 11 Table 9.4. Type of risk characterisation required for man via the environment .................................. 12 Table 9.5. Type of risk characterisation required for workers ............................................................ 13 Table 9.6. Local releases to the environment ................................................................................... 16 Table 9.7. Exposure concentrations and risks for the environment and man via the environment ..... 17 Table 9.8. Local releases to the environment ................................................................................... 18 Table 9.9. Exposure concentrations and risks for the environment and man via the environment ..... 19 Table 9.10. Local releases to the environment ................................................................................. 20 Table 9.11. Exposure concentrations and risks for the environment and man via the environment.... 20 Table 9.12. Exposure concentrations and risks for workers .............................................................. 23 Table 9.13. Exposure concentrations and risks for workers .............................................................. 24 Table 9.14. Exposure concentrations and risks for workers .............................................................. 26 Table 9.15. Exposure concentrations and risks for workers .............................................................. 28 Table 9.16. Exposure concentrations and risks for workers .............................................................. 30 Table 9.17. Exposure concentrations and risks for workers .............................................................. 32 Table 9.18. Exposure concentrations and risks for workers .............................................................. 33 Table 9.19. Exposure concentrations and risks for workers .............................................................. 35 Table 9.20. Exposure concentrations and risks for workers .............................................................. 37 Table 9.21. Exposure concentrations and risks for workers .............................................................. 39 Table 9.22. Local releases to the environment ................................................................................. 41 Table 9.23. Exposure concentrations and risks for the environment and man via the environment.... 42 Table 9.24. Local releases to the environment ................................................................................. 43 Table 9.25. Exposure concentrations and risks for the environment and man via the environment.... 44 Table 9.26. Local releases to the environment ................................................................................. 45 Table 9.27. Exposure concentrations and risks for the environment and man via the environment.... 46 Table 9.28. Exposure concentrations and risks for workers .............................................................. 48 Table 9.29. Exposure concentrations and risks for workers .............................................................. 50 Table 9.30. Local releases to the environment ................................................................................. 52 Table 9.31. Exposure concentrations and risks for the environment and man via the environment.... 53 Table 9.32. Exposure concentrations and risks for workers .............................................................. 55 Table 9.33. Exposure concentrations and risks for workers .............................................................. 57 Table 9.34. Exposure concentrations and risks for workers .............................................................. 59 Table 9.35. Local releases to the environment ................................................................................. 61 Table 9.36. Exposure concentrations and risks for the environment and man via the environment.... 62 Table 9.37. Local releases to the environment ................................................................................. 63 Table 9.38. Exposure concentrations and risks for the environment and man via the environment.... 64 Table 9.39. Local releases to the environment ................................................................................. 65 Table 9.40. Exposure concentrations and risks for the environment and man via the environment.... 65 Table 9.41. Exposure concentrations and risks for workers .............................................................. 68 Table 9.42. Exposure concentrations and risks for workers .............................................................. 69 Table 9.43. Exposure concentrations and risks for workers .............................................................. 71 Table 9.44. Local releases to the environment ................................................................................. 73 Table 9.45. Exposure concentrations and risks for the environment and man via the environment.... 74 Table 9.46. Local releases to the environment ................................................................................. 75 Table 9.47. Exposure concentrations and risks for the environment and man via the environment.... 76
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Table 9.48. Local releases to the environment ................................................................................. 77 Table 9.49. Exposure concentrations and risks for the environment and man via the environment.... 78 Table 9.50. Exposure concentrations and risks for workers .............................................................. 80 Table 9.51. Exposure concentrations and risks for workers .............................................................. 82 Table 9.52. Exposure concentrations and risks for workers .............................................................. 84 Table 9.53. Exposure concentrations and risks for workers .............................................................. 85 Table 9.54. Exposure concentrations and risks for workers .............................................................. 87 Table 9.55. Local releases to the environment ................................................................................. 89 Table 9.56. Exposure concentrations and risks for the environment and man via the environment.... 89 Table 9.57. Local releases to the environment ................................................................................. 91 Table 9.58. Exposure concentrations and risks for the environment and man via the environment.... 91 Table 9.59. Local releases to the environment ................................................................................. 93 Table 9.60. Exposure concentrations and risks for the environment and man via the environment.... 93 Table 9.61. Exposure concentrations and risks for workers .............................................................. 96 Table 9.62. Exposure concentrations and risks for workers .............................................................. 97 Table 9.63. Exposure concentrations and risks for workers .............................................................. 99 Table 9.64. Exposure concentrations and risks for workers ............................................................ 101 Table 9.65. Local releases to the environment ............................................................................... 103 Table 9.66. Exposure concentrations and risks for the environment and man via the environment.. 104 Table 9.67. Local releases to the environment ............................................................................... 105 Table 9.68. Exposure concentrations and risks for the environment and man via the environment.. 105 Table 9.69. Local releases to the environment ............................................................................... 107 Table 9.70. Exposure concentrations and risks for the environment and man via the environment.. 107 Table 9.71. Exposure concentrations and risks for workers ............................................................ 109 Table 9.72. Exposure concentrations and risks for workers ............................................................ 111 Table 9.73. Exposure concentrations and risks for workers ............................................................ 113 Table 9.74. Exposure concentrations and risks for workers ............................................................ 115 Table 9.75. Exposure concentrations and risks for workers ............................................................ 116 Table 9.76. Local releases to the environment ............................................................................... 119 Table 9.77. Exposure concentrations and risks for the environment and man via the environment.. 120 Table 9.78. Local releases to the environment ............................................................................... 121 Table 9.79. Exposure concentrations and risks for the environment and man via the environment.. 122 Table 9.80. Local releases to the environment ............................................................................... 123 Table 9.81. Exposure concentrations and risks for the environment and man via the environment.. 123 Table 9.82. Exposure concentrations and risks for workers ............................................................ 125 Table 9.83. Exposure concentrations and risks for workers ............................................................ 127 Table 9.84. Exposure concentrations and risks for workers ............................................................ 129 Table 9.85. Local releases to the environment ............................................................................... 131 Table 9.86. Exposure concentrations and risks for the environment and man via the environment.. 132 Table 9.87. Local releases to the environment ............................................................................... 133 Table 9.88. Exposure concentrations and risks for the environment and man via the environment.. 133 Table 9.89. Local releases to the environment ............................................................................... 135 Table 9.90. Exposure concentrations and risks for the environment and man via the environment.. 135 Table 9.91. Exposure concentrations and risks for workers ............................................................ 137 Table 9.92. Exposure concentrations and risks for workers ............................................................ 139 Table 9.93. Exposure concentrations and risks for workers ............................................................ 141 Table 9.94. Exposure concentrations and risks for workers ............................................................ 143 Table 9.95. Exposure concentrations and risks for workers ............................................................ 145 Table 9.96. Exposure concentrations and risks for workers ............................................................ 147 Table 9.97. Local releases to the environment ............................................................................... 149 Table 9.98. Exposure concentrations and risks for workers ............................................................ 151
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Table 9.99. Local releases to the environment ............................................................................... 152 Table 9.100. Exposure concentrations and risks for workers .......................................................... 155 Table 9.101. Local releases to the environment ............................................................................. 157 Table 9.102. Exposure concentrations and risks for the environment and man via the environment 158 Table 9.103. Local releases to the environment ............................................................................. 159 Table 9.104. Exposure concentrations and risks for the environment and man via the environment 160 Table 9.105. Local releases to the environment ............................................................................. 161 Table 9.106. Exposure concentrations and risks for the environment and man via the environment 161 Table 9.107. Exposure concentrations and risks for workers .......................................................... 164 Table 9.108. Exposure concentrations and risks for workers .......................................................... 165 Table 9.109. Local releases to the environment ............................................................................. 168 Table 9.110. Exposure concentrations and risks for the environment and man via the environment 168 Table 9.111. Local releases to the environment ............................................................................. 170 Table 9.112. Exposure concentrations and risks for the environment and man via the environment 170 Table 9.113. Local releases to the environment ............................................................................. 172 Table 9.114. Exposure concentrations and risks for the environment and man via the environment 172 Table 9.115. Exposure concentrations and risks for workers .......................................................... 174 Table 9.116. Local releases to the environment ............................................................................. 177 Table 9.117. Exposure concentrations and risks for the environment and man via the environment 178 Table 9.118. Local releases to the environment ............................................................................. 179 Table 9.119. Exposure concentrations and risks for the environment and man via the environment 180 Table 9.120. Exposure concentrations and risks for workers .......................................................... 182 Table 9.121. Exposure concentrations and risks for workers .......................................................... 184 Table 9.122. Exposure concentrations and risks for workers .......................................................... 185 Table 9.123. Exposure concentrations and risks for workers .......................................................... 186 Table 9.124. Exposure concentrations and risks for workers .......................................................... 188 Table 9.125. Local releases to the environment ............................................................................. 189 Table 9.126. Exposure concentrations and risks for workers .......................................................... 191 Table 9.127. Local releases to the environment ............................................................................. 192 Table 9.128. Exposure concentrations and risks for workers .......................................................... 194 Table 9.129. Local releases to the environment ............................................................................. 196 Table 9.130. Exposure concentrations and risks for the environment and man via the environment 197 Table 9.131. Local releases to the environment ............................................................................. 198 Table 9.132. Exposure concentrations and risks for the environment and man via the environment 199 Table 9.133. Local releases to the environment ............................................................................. 200 Table 9.134. Exposure concentrations and risks for the environment and man via the environment 200 Table 9.135. Exposure concentrations and risks for workers .......................................................... 203 Table 9.136. Exposure concentrations and risks for workers .......................................................... 204 Table 9.137. Exposure concentrations and risks for workers .......................................................... 206 Table 9.138. Exposure concentrations and risks for workers .......................................................... 208 Table 9.139. Exposure concentrations and risks for workers .......................................................... 210 Table 9.140. Exposure concentrations and risks for workers .......................................................... 211 Table 9.141. Local releases to the environment ............................................................................. 214 Table 9.142. Exposure concentrations and risks for the environment and man via the environment 214 Table 9.143. Local releases to the environment ............................................................................. 216 Table 9.144. Exposure concentrations and risks for the environment and man via the environment 217 Table 9.145. Local releases to the environment ............................................................................. 218 Table 9.146. Exposure concentrations and risks for the environment and man via the environment 219 Table 9.147. Exposure concentrations and risks for workers .......................................................... 220 Table 9.148. Exposure concentrations and risks for workers .......................................................... 222 Table 9.149. Local releases to the environment ............................................................................. 223
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Table 9.150. Exposure concentrations and risks for workers .......................................................... 225 Table 9.151. Local releases to the environment ............................................................................. 228 Table 9.152. Exposure concentrations and risks for the environment and man via the environment 229 Table 9.153. Local releases to the environment ............................................................................. 230 Table 9.154. Exposure concentrations and risks for the environment and man via the environment 231 Table 9.155. Local releases to the environment ............................................................................. 232 Table 9.156. Exposure concentrations and risks for the environment and man via the environment 233 Table 9.157. Exposure concentrations and risks for workers .......................................................... 235 Table 9.158. Exposure concentrations and risks for workers .......................................................... 237 Table 9.159. Exposure concentrations and risks for workers .......................................................... 239 Table 9.160. Exposure concentrations and risks for workers .......................................................... 240 Table 10.1. Summary of maximum RCRs and sums of RCRs per ES ............................................. 242 Table 10.2. Total releases to the environment per year from all life cycle stages ............................ 243 Table 10.3. Predicted regional exposure concentrations (Regional PEC) and risks for the environment...................................................................................................................................................... 243 Table 10.4. Regional emission of cobalt (kg Co/year) to the different environmental compartments 244 Table 10.5. Continental (EU-27 + Norway) emission of cobalt (kg Co/year) to the different environmental compartments ......................................................................................................... 245 Table 10.6. Calculated PECadd regional for the different environmental compartments.................. 246
Table 10.7. Baseline cobalt concentrations (in g/L) in European surface water (data from FOREGS Geochemical Baseline Program).................................................................................................... 247 Table 10.8.Baseline cobalt concentrations (in mg/kg) in European freshwater sediments (data from FOREGS Geochemical Baseline Program) .................................................................................... 248 Table 10.9. Measured regional PEC values for natural soils in different countries ........................... 249 Table 10.10. Measured regional PEC values for the freshwater in different countries. .................... 250 Table 10.11. Measured regional PEC values for the marine water at different locations.................. 250 Table 10.12. Measured regional PEC values for the freshwater sediments in different countries .... 251 Table 10.13. Measured regional PEC values for the marine sediments at different locations .......... 252 Table 10.14. Measured regional PEC values for grazing soils in different countries ........................ 253 Table 10.15. Measured regional PEC values for agricultural soils in different countries .................. 254
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9. EXPOSURE ASSESSMENT (and related risk characterisation) The sections 9 and 10 of this CSR have been generated with Chesar 3.4.
9.0. Introduction
9.0.1. Overview on uses
See the description of the various uses in section 2 of the CSR.
9.0.2. Assessment entity groups
Not applicable.
9.0.3. Introduction to the assessment for the environment
9.0.3.1. Tonnage
Not applicable.
Table 9.1. Tonnage for assessment
Not applicable.
9.0.3.2. Scope and type of assessment for the environment
The scope of exposure assessment and type of risk characterisation required for the environment are described in the following table based on the hazard conclusions presented in section 7.
Table 9.2. Type of risk characterisation required for the environment
Protection target Risk characterisation type
Hazard conclusion (see section 7)
Fresh water Quantitative PNEC aqua (freshwater) = 0.62 µg/L
Sediment (freshwater) Quantitative PNEC sediment (freshwater) = 53.8 mg/kg sediment dw
Marine water Quantitative PNEC aqua (marine water) = 2.36 µg/L
Sediment (marine water)
Quantitative PNEC sediment (marine water) = 69.8 mg/kg sediment dw
Sewage Treatment Plant
Quantitative PNEC STP = 0.37 mg/L
Air Not needed No hazard identified
Agricultural soil Quantitative PNEC soil = 10.9 mg/kg soil dw
Predator’s prey (freshwater)
Not needed No potential for bioaccumulation
Predator’s prey (marine water)
Not needed No potential for bioaccumulation
Top predator’s prey (marine water)
Not needed No potential for bioaccumulation
Predator’s prey (terrestrial)
Not needed No potential for bioaccumulation
9.0.3.3. Fate and distribution parameters
Physicochemical properties used for exposure estimation
The following substance properties are used in the fate estimation done by EUSES. They correspond
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to the “value used for CSA” reported in sections 1 and 4.
Table 9.3. Substance key phys-chem and fate properties
Substance property Value
Molecular weight ≥ 182.9
Molecular weight used for the assessment 182.9
Vapour pressure 1E-12 Pa at 20 °C
Water solubility 669.6 g/L at 20 °C
Biodegradation in water: screening tests under test conditions no biodegradation observed
Log Kp (solids-water in soil) 3.47
Log Kp (solids water in sediment) 2.94
Log Kp (solids-water in suspended matter) 4.59
Fate (release percentage) in the modelled biological sewage treatment plant
In a standard (modelled) biological STP, the emissions are distributed in the following way:
Release to water 60%
Release to air 0%
Release to sludge 40%
Release degraded 0%
The fractions reported in the above table have been set by the assessor . Explanation: Based on measured release rates.
9.0.3.4. Comments on assessment approach for the environment
The regional concentrations are reported in section 10.2.1.1. The local Predicted Exposure Concentrations (PECs) reported for each contributing scenario correspond to the sum of the local concentrations (Clocal) and the regional concentrations (PEC regional).
ADDED RISK APPROACH Guidance on the how to deal with natural background issues is provided in the Appendix R.7.12-2 guidance document on the ‘Environmental risk for metals and metal compounds’ (ECHA, 2008). In order to deal with the presence of a natural background, various concepts have been developed, such as the Added Risk approach (Added RA) and the Total Risk approach (Total RA) concepts. In essence the Added RA assumes that species are fully adapted to the natural background concentration and therefore that only the anthropogenic added fraction should be regulated or controlled. The Total RA assumes that “exposure” and “effects” should be compared on the combination of the natural background and the added anthropogenic concentrations. According to the FOREGS database, natural background concentrations in the different environmental compartments are very close or even below their respective PNEC values. Indeed, the median background concentration in the EU surface waters (i.e. 0.44 µg/l) is very close to the realistic worst case PNECtotal of 0.70 µg/l; the median background concentration in the EU soils (i.e. 16.1 mg/kg) is above the PNECtotal of 10.1 mg/kg. In those situations where it is expected that background metals concentrations are a significant portion of the derived PNEC, the Added Risk Approach should be applied, therefore the added risk approach was selected in this CSR. Although the median background concentration in the EU freshwater sediment (i.e. 16.5 mg/kg) is below the PNECtotal of 69.8 mg/kg, the Added Risk Approach is also applied for consistency reasons. In the present environmental exposure assessment, the use of the added risk approach implies that the PECadd values have been calculated from cobalt emissions due to anthropogenic activities. Thus, the PECadd is the anthropogenic part of the cobalt concentration in the environment. The predicted cobalt concentrations in the environment with EUSES, which is based on the anthropogenic emissions, therefore reflect the “added” part of the cobalt concentration in the environment. Measured cobalt concentrations could also serve as the basis for the derivation of added environmental exposure concentrations. However, it is known from literature that the natural background
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concentrations of metals may substantially vary seasonally over different geographic regions, therefore hampering the establishment of a “default background concentration” and therefore also the “added risk approach”. In the environmental effects assessment, the use of the added risk approach implies that the PNECadd has been derived from toxicity data that are based on the added cobalt concentration in the tests. Finally, in the environmental risk characterisation, the use of the added risk approach implies the evaluation of the PECadd / PNECadd ratios.
9.0.3.5. Scope and type of assessment for man via environment
The scope of exposure assessment and type of risk characterisation required for man via the environment are described in the following table based on the hazard conclusions presented in section 5.11.
Table 9.4. Type of risk characterisation required for man via the environment
Route of exposure and type of effects
Risk characterisation type
Hazard conclusion (see section 5.11)
Inhalation: Long term, local*
Quantitative DNEL (Derived No Effect Level) = 19.6 µg/m³ DNEL (Derived No Effect Level) = 6.3 µg Co/m³ **
Oral: Long term, Systemic
Quantitative DNEL (Derived No Effect Level) = 92.5 µg/kg bw/day DNEL (Derived No Effect Level) = 29.8 µg Co/kg bw/day**
* The DNEL for long-term inhalation exposure, systemic effects was not derived, because systemic impacts in
long-term rodent inhalation studies are considered to be secondary to local pulmonary toxicity. It is assumed that
the low long-term inhalation DNEL for local effects will prevent significant systemic exposure. No combined risk
characterisation will be provided.
** The exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk
characterisation the DNELs based on cobalt will be used.
9.0.3.6. Comments on assessment approach for man via the environment
For a detailed description of the methodology used for the indirect exposure assessment for men via the environment and the evaluation of data, please refer to the document attached in IUCLID section 13. A brief description is given below:The sources of human exposure to cobalt handled under indirect exposure via the environment are food, water and air. The assessment has been based on cobalt, since this is the toxic species. Cobalt is released to the environment through air effluents and wastewater from manufacture, formulation, processing, use and disposal of cobalt containing products. Cobalt is also a naturally occurring element. Therefore, its presence in the environment, and thereby also indirect in water, food and beverages produced from agricultural goods, may also be attributed to natural sources. Furthermore, cobalt constitutes 4% by weight of vitamin B12, an essential human nutrient.Regarding the ingestion of food, the conventional partitioning-based TGD methodology for determining air-to-soil and soil-to-plant factors in the assessment of human uptake pathways may be considered as mostly inapplicable to metals. Therefore, the HERAG FACT Sheet on indirect exposure via the environment has been considered as guidance. The concentrations in environmental compartments and intake media which are used to derive the daily intake are preferably based on monitored data, since the alternative route by modelling of environmental concentrations is associated with much higher uncertainties and also difficult to apply for metals. In deviation from the TGD food basket approach for the exposure route “ingestion of food”, an assessment of measured and publicly available data on cobalt in the diet was performed and the following study designs have been considered: duplicate meal studies, total diet studies and market basket studies. In duplicate meal studies, duplicate samples of meals, snacks and beverages are collected and analysed. In total diet studies, food items are processed for consumption and are analysed individually or in food groups. Cobalt intake is calculated as the product of the cobalt level in the food and the corresponding amount consumed. In market basket studies, individual food items are sampled from retail outlets (according to typical daily market basket determined from national databases) and subsequently analysed. Based on these cobalt levels and on estimated consumption, total cobalt intake is calculated.EXPOSURE FROM
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FOODAll available published dietary intake studies are based on cobalt levels in food and consumption patterns. As duplicate meal studies were only available for special subpopulations the exposure assessment of cobalt via the diet for adults has been based on the UK total diet study from 1994.- typical exposure: the median value, i.e. 12 µg Co/day - worst-case: the 97.5th percentile, i.e 19 µg Co/day EXPOSURE VIA DRINKING WATERThe concentrations in drinking water are normally taken from regional and local environmental exposure assessment. However, these values refer to surface waters, which are normally not used directly for human consumption. Therefore, cobalt concentrations in drinking water in Europe (regional) are based on measured data which are more precise. An assessment of publicly available data on cobalt in drinking water was performed. The most recent and very comprehensive data source is from Reimann & Birke 2010. In a wide geographical distribution of water sources across 40 European countries, the bottled mineral, drinking and tap waters are characterized. The median (0.023 µg/L) derived in this dataset has been used as a typical cobalt concentration in drinking water in Europe.EXPOSURE VIA AIRCobalt concentrations in air were taken from (a) calculated industrial site emission data (local) and (b) ambient monitoring data (regional), which were taken from the environmental risk assessment.
9.0.4. Introduction to the assessment for workers
9.0.4.1. Scope and type of assessment for workers
The scope of exposure assessment and type of risk characterisation required for workers are described in the following table based on the hazard conclusions presented in section 5.11.
Table 9.5. Type of risk characterisation required for workers
Route Type of effect Risk characterisation type
Hazard conclusion (see section 5.11)
Inhalation
Systemic effects - long term
Not needed No hazard identified
Systemic effects - acute
Not needed No hazard identified
Local effects - long term
Quantitative DNEL (Derived No Effect Level) = 124.2 µg/m³
Local effects - acute
Qualitative High hazard (no threshold derived)
Dermal
Systemic effects - long term
Not needed No hazard identified
Systemic effects - acute
Not needed No hazard identified
Local effects - long term
Qualitative Medium hazard (no threshold derived)
Local effects - acute
Qualitative Medium hazard (no threshold derived)
Eye Local effects Qualitative Medium hazard (no threshold derived)
9.0.4.2. Comments on assessment approach for workers
Assessment approach related to toxicological hazard:
QUANTITATIVE EXPOSURE ASSESSMENT Please refer to IUCLID Section 13 for a detailed description of the specific methodologies used for the worker contributing scenarios below. QUALITATIVE RISK CHARACTERISATION FOR LOCAL EFFECTS ON THE SKIN AND TO THE EYES In addition to the quantitative risk characterisation, demonstrating that prescribed operational conditions and risk management measures effectively control exposure well below the respective chronic DNELs, residual exposure concentrations may theoretically still cause local effects. As a precautionary measure, it is therefore prescribed to use personal protective equipment in situations in which such
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residual exposure concentrations cannot be excluded. The risk of local effects is therefore adequately controlled. QUALITATIVE RISK CHARACTERISATION FOR LOCAL ACUTE EFFECTS VIA INHALATION For acute local effects via inhalation, a semi-quantitative risk assessment was conducted. As a role of thumb, the guidance suggests in such cases to multiply the corresponding chronic DNEL by a factor of 2 in order to derive a surrogate threshold value. Thus, when extrapolating from full-shift exposure levels to peak exposure levels (i.e. multiplying 90th percentile exposure values by a factor of 2 according to ECHA guidance R.14) the same RCR would be calculated for acute effects when compared to peak exposure levels. In addition, RPE is always prescribed on a precautionary basis by taking a minimum assigned protection factor (APF) of 10 available from EN 529 for specific RPE, so that any potential extreme peak exposure levels are also covered.
Assessment approach related to physicochemical hazard:
The substance has oxidising properties, and should not be contacted with acids, reducing agents, flammable materials, combustible material, powdered metal salts and Polyvinylchloride.
9.0.5. Introduction to the assessment for consumers
Exposure assessment is not applicable as there are no consumer-related uses for the substance.
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9.1. Exposure scenario 1: Manufacture - Manufacture of cobalt dinitrate Environment contributing scenario(s):
CS 1 Manufacture of cobalt dinitrate ES1 STP Discharge ERC 1
CS 2 Manufacture of cobalt dinitrate ES2 Direct Discharge ERC 1
CS 3 Manufacture of cobalt dinitrate ES3 Marine Discharge ERC 1
Worker contributing scenario(s):
CS 4 Raw material handling PROC 26, PROC 21; PROC 8b
CS 5 Preparation of raw material PROC 3, PROC 1
CS 6 Wet process PROC 4, PROC 1
CS 7 Hot process PROC 22, PROC 1; PROC 27a
CS 8 Further processing PROC 5, PROC 1
CS 9 Filling of liquids in closed system PROC 2
CS 10 Filling of solutions PROC 8b
CS 11 Handling of powders with moderate dustiness potential PROC 26
CS 12 Handling of powders with high dustiness potential PROC 26
CS 13 Cleaning & Maintenance PROC 28
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment. It is noted that exposure from process steps with feed materials other than the substance is merely reported for the sake of completeness. Please refer to information on safe use for the handling of the individual raw materials for process steps preceding the chemical transformation step.
9.1.1. Env CS 1: Manufacture of cobalt dinitrate ES1 STP Discharge (ERC 1)
9.1.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 1.11 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 400 tonnes/year For the generic exposure scenario a tonnage covering 50% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 9 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
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• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 1E3
9.1.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.6. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 7.5E-3% Release factor after on site RMM: 7.5E-3% Local release rate: 0.083 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 9 companies.
Air Estimated release factor Release factor before on site RMM: 4.52E-3% Release factor after on site RMM: 4.52E-3% Local release rate: 0.05 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 6 companies.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.1.1.3. Exposure and risks for the environment and man via the environment
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The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.7. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 1.16E-4 mg/L RCR = 0.187
Sediment (freshwater) Local PEC: 4.87 mg/kg dw Clocal: 0.61 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.091
Sewage Treatment Plant Local PEC: 0.025 mg/L RCR = 0.068
Agricultural soil Local PEC: 0.946 mg/kg dw RCR = 0.087
Man via environment - Inhalation
Concentration in air: 1.38E-5 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.1.2. Env CS 2: Manufacture of cobalt dinitrate ES2 Direct Discharge (ERC 1)
9.1.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 1.11 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 400 tonnes/year For the generic exposure scenario a tonnage covering 50% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 9 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
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Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 1E3
9.1.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.8. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 7.5E-3% Release factor after on site RMM: 7.5E-3% Local release rate: 0.083 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 9 companies.
Air Estimated release factor Release factor before on site RMM: 4.52E-3% Release factor after on site RMM: 4.52E-3% Local release rate: 0.05 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 6 companies.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.1.2.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
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Table 9.9. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 1.26E-4 mg/L RCR = 0.204
Sediment (freshwater) Local PEC: 5.28 mg/kg dw Clocal: 1.02 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.098
Agricultural soil Local PEC: 0.245 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.38E-5 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.1.3. Env CS 3: Manufacture of cobalt dinitrate ES3 Marine Discharge (ERC 1)
9.1.3.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 1.11 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 400 tonnes/year For the generic exposure scenario a tonnage covering 50% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 9 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use
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and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Marine water only
• Dilution factor to marine water: <= 100
9.1.3.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.10. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 7.5E-3% Release factor after on site RMM: 7.5E-3% Local release rate: 0.083 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 9 companies.
Air Estimated release factor Release factor before on site RMM: 4.52E-3% Release factor after on site RMM: 4.52E-3% Local release rate: 0.05 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 6 companies.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.1.3.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.11. Exposure concentrations and risks for the environment and man via the environment
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Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.195 µg/L Clocal: 0.18 µg/L (estimated by Clocal calculation with Kp susp. matter marine (logKp = 4.94))
RCR = 0.083
Sediment (marine water) Local PEC: 30.43 mg/kg dw Clocal: 15.73 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.436
Agricultural soil Local PEC: 0.245 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.38E-5 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.1.4. Worker CS 4: Raw material handling (PROC 26, PROC 21;
PROC 8b)
Task(s) covered with this contributing scenario: Loading of reaction vessel, immediate removal of wet splashes.
9.1.4.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
• Additional physical form of substance: Massive object Metal chips
Monitoring data
• Additional physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 93 min Monitoring data
• Shifts per year: <= 121 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
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Method
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required. FFP2 mask during powder handling.
Monitoring data
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
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9.1.4.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.12. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 10.3 µg/m³ (Measured data: Monitoring data) RCR = 0.083
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 65 ; GSD: 6.19
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2. Additional remarks on risk characterisation: It is noted that exposure from process steps with feed materials other than the substance is merely reported for the sake of completeness and for precautionary reasons. Any derived exposure estimate and risk characterisation ratio are only applicable if exposure to the substance occurs. Please refer to the specific exposure scenarios for the raw materials used as a downstream use of these substances if the substance is not concerned.
9.1.5. Worker CS 5: Preparation of raw material (PROC 3, PROC 1)
Task(s) covered with this contributing scenario: Weighing, sampling, acid leaching, dissolving, filtration, scraping, purification, cementation, de-ironing (hydrolysis).
9.1.5.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 148 min Monitoring data
• Shifts per year: <= 178 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Maximum process temperature: 95 °C Monitoring data
• Level of containment: Closed reaction vessel Monitoring data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency
Monitoring data
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Method
Reactor equipped with local exhaust ventilation
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.1.5.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.13. Exposure concentrations and risks for workers
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Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 11.4 µg/m³ (Measured data: Monitoring data) RCR = 0.092
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 163 ; GSD: 3.09
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.1.6. Worker CS 6: Wet process (PROC 4, PROC 1)
Task(s) covered with this contributing scenario: Solvent extraction, back stripping, precipitation, drying.
9.1.6.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 120 min Monitoring data
• Shifts per year: <= 122 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
• Level of containment: Closed process Closed pipe system, closed reaction vessels
Monitoring data
• Level of automation: Semi-automated process Monitoring data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency Vapour extraction units in the tank
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to
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Method
be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
Monitoring data
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.1.6.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.14. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 1.6 µg/m³ (Measured data: Monitoring data) RCR = 0.013
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 77 ; GSD: 3.76
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local,
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acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.1.7. Worker CS 7: Hot process (PROC 22, PROC 1; PROC 27a)
Task(s) covered with this contributing scenario: Pyrolysis, calcination.
9.1.7.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Low (temperature based) Only the highest emission potential (EP) is reported. Lower EPs (e.g. if processes are being conducted at lower temperatures in parallel) are thus automatically covered in this assessment.
Monitoring data
• Physical form of substance: Solid Monitoring data
• Additional physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 53 min Monitoring data
• Shifts per year: <= 51 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Exterior local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 86%] High efficiency Extraction device in the surrounding calcination area
Monitoring data
• Level of containment: Closed furnace Monitoring data
• Process temperature: Elevated Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-
Monitoring data
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Method
interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.1.7.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.15. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 6.1 µg/m³ (Measured data: Monitoring data) RCR = 0.049
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 25 ; GSD: 3.67
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.1.8. Worker CS 8: Further processing (PROC 5, PROC 1)
Task(s) covered with this contributing scenario: Blending, milling, sieving.
9.1.8.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: High (abrasion based) Only the highest emission potential (EP) is reported. Lower EPs (e.g. if
Monitoring data
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Method
processes resulting in lower abrasion are being conducted in parallel) are thus automatically covered in this assessment.
• Physical form of substance: Solid, powder / dust Monitoring data
• Additional physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 295 min Monitoring data
• Shifts per year: <= 124 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Level of containment: Closed process Closed transfer system, closed mill
Monitoring data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency
Monitoring data
• Process temperature: Ambient Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Respiratory protective equipment (RPE): RPE with minimum APF = 20 [Effectiveness Inhalation: 95%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P3 with mask according to EN 140, EN 1827 or filtering half mask (FF P3) according to EN 149 or combination of P2 filter with face piece according to EN 12941 or EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
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Method
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.1.8.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.16. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 22.8 µg/m³ (Measured data: Monitoring data) RCR = 0.184
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 75 ; GSD: 5.43
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.1.9. Worker CS 9: Filling of liquids in closed system (PROC 2)
Task(s) covered with this contributing scenario: Filling of solutions in closed system, control walks, supervision and adjusting machinery.
9.1.9.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential: Very low Only the highest emission potential (EP) of the substance in this process is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel or if the actual process temperature or the level of abrasion is lower) are thus automatically covered in this assessment.
MEASE 1.02.01
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
MEASE 1.02.01
• Physical form of substance: Aqueous solution MEASE 1.02.01
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 15 min MEASE 1.02.01
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted
MEASE 1.02.01
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Method
considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Technical and organisational conditions and measures
• Level of containment: Closed process MEASE 1.02.01
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
MEASE 1.02.01
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.1.9.2. Exposure and risks for workers
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The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.17. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.031 µg/m³ (MEASE 1.02.01) RCR < 0.01
Remarks on exposure data from external estimation tools:
MEASE 1.02.01: Explanation: Duration of exposure was not reflected in the exposure estimate by using the assessment tool but instead a linear interpolation was applied to the full-shift estimate as derived by the tool.
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.1.10. Worker CS 10: Filling of solutions (PROC 8b)
Task(s) covered with this contributing scenario: Filling, immediate removal of wet splashes.
9.1.10.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential: Very low Only the highest emission potential (EP) of the substance in this process is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel or if the actual process temperature or the level of abrasion is lower) are thus automatically covered in this assessment.
MEASE 1.02.01
• Physical form of substance: Aqueous solution MEASE 1.02.01
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 30 min MEASE 1.02.01
• Shifts per year: <= 80 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
MEASE 1.02.01
Technical and organisational conditions and measures
• Process temperature: Ambient MEASE 1.02.01
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices MEASE 1.02.01
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Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.1.10.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.18. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.6 µg/m³ (MEASE 1.02.01) RCR < 0.01
Remarks on exposure data from external estimation tools:
MEASE 1.02.01: Explanation: Duration of exposure was not reflected in the exposure estimate by using the assessment tool but instead a linear interpolation was applied to the full-shift estimate as derived by the tool.
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.1.11. Worker CS 11: Handling of powders with moderate dustiness potential (PROC 26)
Task(s) covered with this contributing scenario: Drying, packaging.
9.1.11.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 139 min Monitoring data
• Shifts per year: <= 94 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency
Monitoring data
• Process temperature: Ambient Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below,
Monitoring data
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Method
certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.1.11.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.19. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 13.4 µg/m³ (Measured data: Monitoring data) RCR = 0.108
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 147 ; GSD: 4.55
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.1.12. Worker CS 12: Handling of powders with high dustiness potential (PROC 26)
Task(s) covered with this contributing scenario: Packaging.
9.1.12.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: High Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus
Monitoring data
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Method
automatically covered in this assessment.
• Physical form of substance: Solid, powder / dust Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 139 min Monitoring data
• Shifts per year: <= 94 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency
Monitoring data
• Process temperature: Ambient Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• Respiratory protective equipment (RPE): RPE with minimum APF = 40 [Effectiveness Inhalation: 97.5%] APF = assigned protection factor according to EN 529. At minimum combination of particle filter class P3 with face piece according to EN 136, EN 12941 or EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to
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Method
the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.1.12.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.20. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 18.7 µg/m³ (Measured data: Monitoring data) RCR = 0.151
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 91 ; GSD: 5.96
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.1.13. Worker CS 13: Cleaning & Maintenance (PROC 28)
Task(s) covered with this contributing scenario: Manual cleaning, repair and maintenance operations; Removal of residuals from e.g. filters/overspill or as waste.
9.1.13.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: High Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 94 min Monitoring data
• Shifts per year: <= 122 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
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Method
• Process pressure: Ambient Monitoring data
• Additional operational conditions for cleaning and maintenance: Maintenance and repair work only at machinery/systems which are not in operation. Minor cleaning tasks may be conducted under operation.
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face
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Method
protection may be required to be worn in such cases as appropriate.)
9.1.13.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.21. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 6.7 µg/m³ (Measured data: Monitoring data) RCR = 0.054
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 187 ; GSD: 4.44
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.2. Exposure scenario 2: Manufacture - Manufacture of cobalt nitrate within catalyst or catalyst precursors Environment contributing scenario(s):
CS 1 Manufacture of cobalt nitrate within catalyst or catalyst precursors ES1 STP Discharge
ERC 1
CS 2 Manufacture of cobalt nitrate within catalyst or catalyst precursors ES2 Direct Discharge
ERC 1
CS 3 Manufacture of cobalt nitrate within catalyst or catalyst precursors ES3 Marine Discharge
ERC 1
Worker contributing scenario(s):
CS 4 M1 Dissolution of cobalt metal to form cobalt dinitrate PROC 3, PROC 2; PROC 9
CS 5 MNCM: Cleaning and maintenance PROC 28
Further description of the use:
A variety of Co containing compounds are used in the production of Co containing catalysts. Please note that for environment, very often, emissions cannot be allocated to a distinct activity or process merely because emissions are treated in a central treatment plant and discharged as a single stream (e.g. wastewater emissions). As a consequence, the environmental exposure estimates relate to the Co-ion originating from the production and use of Co compounds in the catalyst industry. A sector approach is taken instead of a substance approach. General process description (Source: ECMA, GES mapping, version 31/10/2014) - Raw materials delivery and handling: bulk delivery of solid raw materials (e.g. tank, silo, car); semi-bulk delivery of solid raw materials (e.g. bags, drums), delivery of liquid raw materials, storage of solid and liquid raw materials, transfer of raw materials from delivery containers into container or central supply system, conveying raw materials (transport to machine for processing). - Catalyst manufacture: dissolving, precipitating, filtrating, drying/heat treatment, mixing, forming, impregnation (continuous, batch), calcination (oxidation at elevated temperatures), reduction, stabilisation, screening (adjusting particle size distribution) - Fresh catalyst packaging: filling operations (transfer to transport containers) - Cleaning and maintenance - Fresh catalyst storage: final product storage
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment. It is noted that this exposure scenario focusses on exposure to the substance to be registered. Please refer to information on safe use for the handling of the individual raw materials for process steps preceding the chemical transformation step.
9.2.1. Env CS 1: Manufacture of cobalt nitrate within catalyst or catalyst precursors ES1 STP Discharge (ERC 1)
9.2.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.272 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 98 tonnes/year For the generic exposure scenario a tonnage covering 90% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 5 companies.
Technical and organisational conditions and measures
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• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 100
9.2.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.22. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 7.4E-3% Release factor after on site RMM: 7.4E-3% Local release rate: 0.02 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 6 companies.
Air Estimated release factor Release factor before on site RMM: 2.2E-3% Release factor after on site RMM: 2.2E-3% Local release rate: 5.98E-3 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 7 companies.
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Release Release estimation method
Explanations
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.2.1.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.23. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 1.38E-4 mg/L RCR = 0.223
Sediment (freshwater) Local PEC: 5.73 mg/kg dw Clocal: 1.47 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.107
Sewage Treatment Plant Local PEC: 6.04E-3 mg/L RCR = 0.016
Agricultural soil Local PEC: 0.409 mg/kg dw RCR = 0.038
Man via environment - Inhalation
Concentration in air: 1.64E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.2.2. Env CS 2: Manufacture of cobalt nitrate within catalyst or catalyst precursors ES2 Direct Discharge (ERC 1)
9.2.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.272 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 98 tonnes/year For the generic exposure scenario a tonnage covering 90% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 5
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companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 245 m3/day The selected effluent discharge rate is the median based on data from 6 companies.
• Dilution factor to freshwater: <= 500
• Discharge to: Freshwater only
9.2.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.24. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 7.4E-3% Release factor after on site RMM: 7.4E-3% Local release rate: 0.02 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 6 companies.
Air Estimated release factor Release factor before on site RMM: 2.2E-3% Release factor after on site RMM: 2.2E-3% Local release rate: 5.98E-3 kg/day Explanation: This release factor is based on reported emissions after
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Release Release estimation method
Explanations
on-site treatment. The selected value is the 50th percentile of 7 companies.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.2.2.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.25. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.04E-4 mg/L RCR = 0.329
Sediment (freshwater) Local PEC: 8.26 mg/kg dw Clocal: 4 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.154
Agricultural soil Local PEC: 0.24 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.64E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.2.3. Env CS 3: Manufacture of cobalt nitrate within catalyst or catalyst precursors ES3 Marine Discharge (ERC 1)
9.2.3.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.272 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 98 tonnes/year For the generic exposure scenario a tonnage covering 90% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year
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The selected number of production days per year is the median value based on data from 5 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 245 m3/day The selected effluent discharge rate is the 70th percentile based on data from 6 companies.
• Discharge to: Marine water only
• Dilution factor to marine water: <= 100
9.2.3.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.26. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 7.4E-3% Release factor after on site RMM: 7.4E-3% Local release rate: 0.02 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 6 companies.
Air Estimated release factor Release factor before on site RMM: 2.2E-3% Release factor after on site RMM: 2.2E-3% Local release rate: 5.98E-3 kg/day Explanation:
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Release Release estimation method
Explanations
This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 7 companies.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.2.3.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.27. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.372 µg/L Clocal: 0.357 µg/L (estimated by Clocal calculation with Kp susp. matter marine (logKp = 4.94))
RCR = 0.158
Sediment (marine water) Local PEC: 45.44 mg/kg dw Clocal: 30.74 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.651
Agricultural soil Local PEC: 0.24 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.64E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.2.4. Worker CS 4: M1 Dissolution of cobalt metal to form cobalt dinitrate (PROC 3, PROC 2; PROC 9)
Task(s) covered with this contributing scenario: Addition of reagents, dissolution, sampling.
9.2.4.1. Conditions of use
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Method
Product (article) characteristics
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Aqueous solution Monitoring data
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Additional physical form of substance: Solid, powder / dust Pellets, briquettes
Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 45 min Monitoring data
• Shifts per year: <= 150 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Maximum process temperature: 160 °C Monitoring data
• Level of containment: Semi-closed process Automated sampling operation.
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
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Method
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.2.4.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.28. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 1.7 µg/m³ (Measured data: Monitoring data) RCR = 0.014
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 2.96
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.2.5. Worker CS 5: MNCM: Cleaning and maintenance (PROC 28)
Task(s) covered with this contributing scenario: Cleaning and maintenance. Manual cleaning, repair and maintenance operations; Removal of residuals from e.g. filters/overspill or as waste. Maintenance and repair work only at facilities which are not in operation. Minor cleaning tasks may be conducted under operation.
9.2.5.1. Conditions of use
Method
Product (article) characteristics
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Maximum emission potential of the substance: Low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus
Monitoring data
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Method
automatically covered in this assessment.
• Physical form of substance: Various Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 120 min Monitoring data
• Shifts per year: <= 48 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
• Process pressure: Ambient Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process)
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Method
and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE): RPE with minimum APF = 20 [Effectiveness Inhalation: 95%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P3 with mask according to EN 140, EN 1827 or filtering half mask (FF P3) according to EN 149 or combination of P2 filter with face piece according to EN 12941 or EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
9.2.5.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.29. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 3.8 µg/m³ (Measured data: Monitoring data) RCR = 0.031
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 26 ; GSD: 4.07
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.3. Exposure scenario 3: Use at industrial sites - Manufacture of cobalt carboxylates and resinates (intermediate use) Market sector: Manufacture of other cobalt substances (intermediate use) Sector of use: SU 8: Manufacture of bulk, large scale chemicals (including petroleum products); SU 9: Manufacture of fine chemicals
Environment contributing scenario(s):
CS 1 Manufacture of cobalt carboxylates and resinates (intermediate use)
ERC 6a
Worker contributing scenario(s):
CS 2 Raw material handling PROC 26, PROC 8b
CS 3 Reaction PROC 4, PROC 1; PROC 3
CS 4 Cleaning & Maintenance PROC 28
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment. It is noted that this exposure scenario focusses on exposure to the registered substance. Please refer to information on safe use for the handling of the individual manufactured substances for process steps commencing the chemical transformation step.
9.3.1. Env CS 1: Manufacture of cobalt carboxylates and resinates (intermediate use) (ERC 6a)
9.3.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 1.8 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 250 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: The majority of the sites do not have emissions to air, the process is enclosed and the manufacture is in a liquid medium. In case emissions to air are still applicable, one or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: The majority of the sites do not have emissions to water, liquid waste resulting from the manufacture of cobalt carboxylates is collected and disposed of to a specialized treatment company. In case emissions to water are still applicable, one or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Site specific [Effectiveness Water: 40%]
• Discharge rate of STP: >= 4E4 m3/day
• Application of the STP sludge on agricultural soil: Yes
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Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 10
Fate (release percentage) in the biological sewage treatment plant
The biological STP is site specific and the releases to the various compartments have been set by the assessor They are distributed in the following way:
Release to water 60%
Release to air 0%
Release to sludge 40%
Release degraded 0%
Explanation: Based on measured information
9.3.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.30. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 5.6E-3% Release factor after on site RMM: 5.6E-3% Local release rate: 0.101 kg/day Explanation: This release factor is based on reported emissions after on-site treatment but before treatment in a municipal STP. Note that most sites do not have emissions to water.
Air Estimated release factor Release factor before on site RMM: 1E-4% Release factor after on site RMM: 1E-4% Local release rate: 1.8E-3 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. These emissions are related to cobalt carboxylates in solid form.
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Release Release estimation method
Explanations
Note that most sites do not have emissions to air.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.3.1.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.31. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 1.95E-4 mg/L RCR = 0.315
Sediment (freshwater) Local PEC: 7.99 mg/kg dw Clocal: 3.73 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
RCR = 0.149
Sewage Treatment Plant Local PEC: 1.51E-3 mg/L RCR < 0.01
Agricultural soil Local PEC: 0.282 mg/kg dw RCR = 0.026
Man via environment - Inhalation
Concentration in air: 1.9E-7 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.3.2. Worker CS 2: Raw material handling (PROC 26, PROC 8b)
Task(s) covered with this contributing scenario: Raw material handling, reactor loading, immediate removal of wet splashes.
9.3.2.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if
Monitoring data
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Method
materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
• Additional physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Monitoring data
• Shifts per year: <= 110 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• Respiratory protective equipment (RPE): RPE with minimum APF = 20 [Effectiveness Inhalation: 95%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P3 with mask according to EN 140, EN 1827 or filtering half mask (FF P3) according to EN 149 or combination of P2 filter with face piece according to EN 12941 or EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
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Method
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.3.2.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.32. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 26.6 µg/m³ (Measured data: Monitoring data) RCR = 0.214
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 28 ; GSD: 5.17
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.3.3. Worker CS 3: Reaction (PROC 4, PROC 1; PROC 3)
Task(s) covered with this contributing scenario: Wet process, dry process, mixing, dissolving, precipitation, separation, filtration, pumping, cleaning, unloading, reaction, stripping, extraction, formulation. It is noted that the substance is used as an intermediate so that the substance is chemically transformed into another substance in this step.
9.3.3.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Analogous data
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• Physical form of substance: Aqueous solution Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Analogous data
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Maximum process temperature: 180 °C Analogous data
• Level of containment: Closed process Closed transfer systems, closed reactor and vacuum scrubbing system
Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE
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Method
protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.3.3.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.33. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 6 µg/m³ (Measured data: Analogous data) RCR = 0.048
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 133 ; GSD: 2.56
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.3.4. Worker CS 4: Cleaning & Maintenance (PROC 28)
Task(s) covered with this contributing scenario: Manual cleaning, repair and maintenance operations; Removal of residuals from e.g. filters/overspill or as waste.
9.3.4.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: High Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Monitoring data
• Shifts per year: <= 48 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
• Process pressure: Ambient Monitoring data
• Additional operational conditions for cleaning and maintenance: Maintenance and repair work only at machinery/systems which are not in operation. Minor cleaning tasks may be conducted under operation.
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
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Method
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• Respiratory protective equipment (RPE): RPE with minimum APF = 20 [Effectiveness Inhalation: 95%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P3 with mask according to EN 140, EN 1827 or filtering half mask (FF P3) according to EN 149 or combination of P2 filter with face piece according to EN 12941 or EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.3.4.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
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Table 9.34. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 17.0 µg/m³ (Measured data: Monitoring data) RCR = 0.137
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 187 ; GSD: 4.44
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.4. Exposure scenario 4: Use at industrial sites - Manufacture of chemicals and in other wet-chemical processes as intermediate Market sector: Manufacture of other cobalt substances (intermediate use) Sector of use: SU 8: Manufacture of bulk, large scale chemicals (including petroleum products); SU 9: Manufacture of fine chemicals
Environment contributing scenario(s):
CS 1 Manufacture of chemicals and in other wet-chemical processes as intermediate ES1 STP Discharge
ERC 6a
CS 2 Manufacture of chemicals and in other wet-chemical processes as intermediate ES2 Direct Discharge
ERC 6a
CS 3 Manufacture of chemicals and in other wet-chemical processes as intermediate ES3 Marine Discharge
ERC 6a
Worker contributing scenario(s):
CS 4 Raw material handling PROC 26, PROC 8b; PROC 9
CS 5 Mixing/Reaction in vessel/bath PROC 3, PROC 1; PROC 2; PROC 4; PROC 5
CS 6 Cleaning & Maintenance PROC 28
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment. It is noted that this exposure scenario focusses on exposure to the registered substance. Please refer to information on safe use for the handling of the individual manufactured substances for process steps commencing the chemical transformation step.
9.4.1. Env CS 1: Manufacture of chemicals and in other wet-chemical processes as intermediate ES1 STP Discharge (ERC 6a)
9.4.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 1.11 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 400 tonnes/year For the generic exposure scenario a tonnage covering 50% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 9 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
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• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Dilution factor to freshwater: <= 1E3
• Discharge to: Freshwater only
9.4.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.35. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 7.5E-3% Release factor after on site RMM: 7.5E-3% Local release rate: 0.083 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 9 companies.
Air Estimated release factor Release factor before on site RMM: 4.52E-3% Release factor after on site RMM: 4.52E-3% Local release rate: 0.05 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 6 companies.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.4.1.3. Exposure and risks for the environment and man via the environment
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The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.36. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 1.16E-4 mg/L RCR = 0.187
Sediment (freshwater) Local PEC: 4.87 mg/kg dw Clocal: 0.61 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.091
Sewage Treatment Plant Local PEC: 0.025 mg/L RCR = 0.068
Agricultural soil Local PEC: 0.946 mg/kg dw RCR = 0.087
Man via environment - Inhalation
Concentration in air: 1.38E-5 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.4.2. Env CS 2: Manufacture of chemicals and in other wet-chemical processes as intermediate ES2 Direct Discharge (ERC 6a)
9.4.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 1.11 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 400 tonnes/year For the generic exposure scenario a tonnage covering 50% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 9 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
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Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Dilution factor to freshwater: <= 1E3
• Discharge to: Freshwater only
9.4.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.37. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 7.5E-3% Release factor after on site RMM: 7.5E-3% Local release rate: 0.083 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 9 companies.
Air Estimated release factor Release factor before on site RMM: 4.52E-3% Release factor after on site RMM: 4.52E-3% Local release rate: 0.05 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 6 companies.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.4.2.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
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Table 9.38. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 1.26E-4 mg/L RCR = 0.204
Sediment (freshwater) Local PEC: 5.28 mg/kg dw Clocal: 1.02 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.098
Agricultural soil Local PEC: 0.245 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.38E-5 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.4.3. Env CS 3: Manufacture of chemicals and in other wet-chemical processes as intermediate ES3 Marine Discharge (ERC
6a)
9.4.3.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 1.11 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 400 tonnes/year For the generic exposure scenario a tonnage covering 50% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 9 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
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• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Marine water only
• Dilution factor to marine water: <= 100
9.4.3.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.39. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 7.5E-3% Release factor after on site RMM: 7.5E-3% Local release rate: 0.083 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 9 companies.
Air Estimated release factor Release factor before on site RMM: 4.52E-3% Release factor after on site RMM: 4.52E-3% Local release rate: 0.05 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 6 companies.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.4.3.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.40. Exposure concentrations and risks for the environment and man via the
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environment
Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.195 µg/L Clocal: 0.18 µg/L (estimated by Clocal calculation with Kp susp. matter marine (logKp = 4.94))
RCR = 0.083
Sediment (marine water) Local PEC: 30.43 mg/kg dw Clocal: 15.73 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.436
Agricultural soil Local PEC: 0.245 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.38E-5 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.4.4. Worker CS 4: Raw material handling (PROC 26, PROC 8b; PROC 9)
Task(s) covered with this contributing scenario: Loading/unloading, weighing, immediate removal of wet splashes.
9.4.4.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Analogous data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Analogous data
• Physical form of substance: Solid, crystal Analogous data
• Additional physical form of substance: Aqueous solution Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 150 min Analogous data
• Shifts per year: <= 82 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
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Method
• Process temperature: Ambient Analogous data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency
Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Analogous data
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face
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protection may be required to be worn in such cases as appropriate.)
9.4.4.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.41. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 14.5 µg/m³ (Measured data: Analogous data) RCR = 0.117
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 147 ; GSD: 4.55
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.4.5. Worker CS 5: Mixing/Reaction in vessel/bath (PROC 3, PROC 1; PROC 2; PROC 4; PROC 5)
Task(s) covered with this contributing scenario: Mixing, blending, reaction, formulation, electro-winning, sampling. It is noted that the substance is used as an intermediate so that the substance is chemically transformed into another substance in this step.
9.4.5.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Analogous data
• Physical form of substance: Aqueous solution Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 15 min Analogous data
• Shifts per year: <= 80 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process temperature: Elevated Analogous data
• Level of containment: Closed process Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous
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supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.4.5.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.42. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.2 µg/m³ (Measured data: Analogous data) RCR < 0.01
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Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 133 ; GSD: 2.56
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.4.6. Worker CS 6: Cleaning & Maintenance (PROC 28)
Task(s) covered with this contributing scenario: Manual cleaning, repair and maintenance operations, removal of residuals from e.g. filters/overspill or as waste.
9.4.6.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: High Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Physical form of substance: Solid, powder / dust Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 18 min Analogous data
• Shifts per year: <= 78 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
• Process pressure: Ambient Analogous data
• Additional operational conditions for cleaning and maintenance: Maintenance and repair work only at machinery/systems which are not in operation. Minor cleaning tasks may be conducted under operation.
Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Analogous data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as
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appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.4.6.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.43. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 1.2 µg/m³ (Measured data: Analogous data) RCR = 0.01
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 187 ; GSD: 4.44
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.5. Exposure scenario 5: Use at industrial sites - Industrial use of RM as intermediate for the production of another substance in catalyst or catalyst precursor manufacture Market sector: Manufacture of other cobalt substances (intermediate use) Sector of use: SU 8: Manufacture of bulk, large scale chemicals (including petroleum products); SU 9: Manufacture of fine chemicals
Environment contributing scenario(s):
CS 1 Industrial use of RM as intermediate for the production of another substance in catalyst or catalyst precursor manufacture ES1 STP Discharge
ERC 6a
CS 2 Industrial use of RM as intermediate for the production of another substance in catalyst or catalyst precursor manufacture ES2 Direct Discharge
ERC 6a
CS 3 Industrial use of RM as intermediate for the production of another substance in catalyst or catalyst precursor manufacture ES3 Marine Discharge
ERC 6a
Worker contributing scenario(s):
CS 4 N1: Delivery and storage of cobalt nitrate raw material PROC 8b, PROC 3; PROC 4; PROC 9
CS 5 N2: Dissolution of cobalt nitrate raw material PROC 3, PROC 9
CS 6 N3: Impregnation, drying & calcination of cobalt nitrate PROC 4, PROC 1; PROC 2; PROC 3
CS 7 N4: Precipitation of cobalt carbonate from cobalt nitrate solution
PROC 3, PROC 9
CS 8 NCM: Cleaning and maintenance PROC 28
Further description of the use:
A variety of Co containing compounds are used in the production of Co containing catalysts. Please note that for environment, very often, emissions cannot be allocated to a distinct activity or process merely because emissions are treated in a central treatment plant and discharged as a single stream (e.g. wastewater emissions). As a consequence, the environmental exposure estimates relate to the Co-ion originating from the production and use of Co compounds in the catalyst industry. A sector approach is taken instead of a substance approach. General process description (Source: ECMA, GES mapping, version 31/10/2014) - Raw materials delivery and handling: bulk delivery of solid raw materials (e.g. tank, silo, car); semi-bulk delivery of solid raw materials (e.g. bags, drums), delivery of liquid raw materials, storage of solid and liquid raw materials, transfer of raw materials from delivery containers into container or central supply system, conveying raw materials (transport to machine for processing). - Catalyst manufacture: dissolving, precipitating, filtrating, drying/heat treatment, mixing, forming, impregnation (continuous, batch), calcination (oxidation at elevated temperatures), reduction, stabilisation, screening (adjusting particle size distribution) - Fresh catalyst packaging: filling operations (transfer to transport containers) - Cleaning and maintenance
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment. It is noted that this exposure scenario focusses on exposure to the registered substance. Please refer to information on safe use for the handling of the individual manufactured substances for process steps commencing the chemical transformation step.
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9.5.1. Env CS 1: Industrial use of RM as intermediate for the production of another substance in catalyst or catalyst precursor manufacture ES1 STP Discharge (ERC 6a)
9.5.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.272 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 98 tonnes/year For the generic exposure scenario a tonnage covering 90% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 5 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 100
9.5.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.44. Local releases to the environment
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Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 7.4E-3% Release factor after on site RMM: 7.4E-3% Local release rate: 0.02 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 6 companies.
Air Estimated release factor Release factor before on site RMM: 2.2E-3% Release factor after on site RMM: 2.2E-3% Local release rate: 5.98E-3 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 7 companies.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.5.1.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.45. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 1.38E-4 mg/L RCR = 0.223
Sediment (freshwater) Local PEC: 5.73 mg/kg dw Clocal: 1.47 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
RCR = 0.107
Sewage Treatment Plant Local PEC: 6.04E-3 mg/L RCR = 0.016
Agricultural soil Local PEC: 0.409 mg/kg dw RCR = 0.038
Man via environment - Inhalation
Concentration in air: 1.64E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such
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for the risk characterisation the DNELs based on cobalt were used.
9.5.2. Env CS 2: Industrial use of RM as intermediate for the production of another substance in catalyst or catalyst precursor manufacture ES2 Direct Discharge (ERC 6a)
9.5.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.272 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 98 tonnes/year For the generic exposure scenario a tonnage covering 90% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 5 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 245 m3/day The selected effluent discharge rate is the 70th percentile based on data from 6 companies.
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 500
9.5.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.46. Local releases to the environment
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Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 7.4E-3% Release factor after on site RMM: 7.4E-3% Local release rate: 0.02 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 6 companies.
Air Estimated release factor Release factor before on site RMM: 2.2E-3% Release factor after on site RMM: 2.2E-3% Local release rate: 5.98E-3 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 7 companies.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.5.2.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.47. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.04E-4 mg/L RCR = 0.329
Sediment (freshwater) Local PEC: 8.26 mg/kg dw Clocal: 4 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
RCR = 0.154
Agricultural soil Local PEC: 0.24 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.64E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
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9.5.3. Env CS 3: Industrial use of RM as intermediate for the production of another substance in catalyst or catalyst precursor manufacture ES3 Marine Discharge (ERC 6a)
9.5.3.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.272 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 98 tonnes/year For the generic exposure scenario a tonnage covering 90% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 5 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 245 m3/day The selected effluent discharge rate is the 70th percentile based on data from 6 companies.
• Discharge to: Marine water only
• Dilution factor to marine water: <= 100
9.5.3.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.48. Local releases to the environment
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Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 7.4E-3% Release factor after on site RMM: 7.4E-3% Local release rate: 0.02 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 6 companies.
Air Estimated release factor Release factor before on site RMM: 2.2E-3% Release factor after on site RMM: 2.2E-3% Local release rate: 5.98E-3 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 7 companies.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.5.3.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.49. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.372 µg/L Clocal: 0.357 µg/L (estimated by Clocal calculation with Kp susp. matter marine (logKp = 4.94))
RCR = 0.158
Sediment (marine water) Local PEC: 45.46 mg/kg dw Clocal: 30.76 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
RCR = 0.651
Agricultural soil Local PEC: 0.24 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.64E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from
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food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.5.4. Worker CS 4: N1: Delivery and storage of cobalt nitrate raw material (PROC 8b, PROC 3; PROC 4; PROC 9)
Task(s) covered with this contributing scenario: Delivery, transfer, storage.
9.5.4.1. Conditions of use
Method
Product (article) characteristics
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Solid, crystal Monitoring data
• Additional physical form of substance: Aqueous solution Monitoring data
• Maximum emission potential of the substance: Low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 230 min Monitoring data
• Shifts per year: <= 18 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Level of containment Closed process or open process with generic local exhaust ventilation
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Certified safety clothing and shoes
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Method
Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.5.4.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.50. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 4.3 µg/m³ (Measured data: Monitoring data) RCR = 0.035
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 27 ; GSD: 2.18
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.5.5. Worker CS 5: N2: Dissolution of cobalt nitrate raw material (PROC 3, PROC 9)
Task(s) covered with this contributing scenario: Addition of reagents, dissolution, sampling.
9.5.5.1. Conditions of use
Method
Product (article) characteristics
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Solid, crystal Monitoring data
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Method
• Additional physical form of substance: Aqueous solution Monitoring data
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 120 min Monitoring data
• Shifts per year: <= 5 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Level of containment: Closed process Fully automated addition of reagents and dissolution.
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Eye protection: Eye protection to be worn to protect from eye damage Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as
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Method
appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Respiratory protective equipment (RPE): RPE with minimum APF = 20 [Effectiveness Inhalation: 95%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P3 with mask according to EN 140, EN 1827 or filtering half mask (FF P3) according to EN 149 or combination of P2 filter with face piece according to EN 12941 or EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
9.5.5.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.51. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.2 µg/m³ (Measured data: Monitoring data) RCR < 0.01
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 2.96
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.5.6. Worker CS 6: N3: Impregnation, drying & calcination of cobalt nitrate (PROC 4, PROC 1; PROC 2; PROC 3)
Task(s) covered with this contributing scenario: Addition of reagents, impregnation, transfer to dryer/calciner, drying/calcination.
9.5.6.1. Conditions of use
Method
Product (article) characteristics
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Aqueous solution Monitoring data
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 40 min Monitoring data
• Shifts per year: <= 14 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
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Method
Technical and organisational conditions and measures
• Level of containment: Semi-closed process Monitoring data
• Level of containment: Closed process Calcination is conducted in closed processes.
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.5.6.2. Exposure and risks for workers
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The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.52. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 2.7 µg/m³ (Measured data: Monitoring data) RCR = 0.022
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 4 ; GSD: 2.23
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.5.7. Worker CS 7: N4: Precipitation of cobalt carbonate from cobalt nitrate solution (PROC 3, PROC 9)
Task(s) covered with this contributing scenario: Addition of reagents, precipitation, sampling.
9.5.7.1. Conditions of use
Method
Product (article) characteristics
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Aqueous solution Monitoring data
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 10 min Monitoring data
• Shifts per year: <= 45 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Level of containment: Closed process Sampling may be conducted in semi-closed processes.
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice
Monitoring data
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Method
and proper use of personal protective equipment (if relevant) is required.
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Respiratory protective equipment (RPE): RPE with minimum APF = 20 [Effectiveness Inhalation: 95%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P3 with mask according to EN 140, EN 1827 or filtering half mask (FF P3) according to EN 149 or combination of P2 filter with face piece according to EN 12941 or EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
9.5.7.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.53. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.03 µg/m³ (Measured data: Monitoring data) RCR < 0.01
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 4 ; GSD: 2.23
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local):
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Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.5.8. Worker CS 8: NCM: Cleaning and maintenance (PROC 28)
Task(s) covered with this contributing scenario: Cleaning and maintenance. Manual cleaning, repair and maintenance operations; Removal of residuals from e.g. filters/overspill or as waste. Maintenance and repair work only at facilities which are not in operation. Minor cleaning tasks may be conducted under operation.
9.5.8.1. Conditions of use
Method
Product (article) characteristics
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Maximum emission potential of the substance: Low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Physical form of substance: Various Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 120 min Monitoring data
• Shifts per year: <= 48 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
• Process pressure: Ambient Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
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Method
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• Respiratory protective equipment (RPE): RPE with minimum APF = 20 [Effectiveness Inhalation: 95%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P3 with mask according to EN 140, EN 1827 or filtering half mask (FF P3) according to EN 149 or combination of P2 filter with face piece according to EN 12941 or EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
9.5.8.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.54. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 3.8 µg/m³ (Measured data: Monitoring data) RCR = 0.031
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 26 ; GSD: 4.07
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.6. Exposure scenario 6: Formulation or re-packing - Formulation of metal surface treatment pre-formulations Market sector: Use in surface treatment Product category formulated: PC 14: Metal surface treatment products
Environment contributing scenario(s):
CS 1 Formulation of metal surface treatment pre-formulations ES1 STP Discharge
ERC 2
CS 2 Formulation of metal surface treatment pre-formulations ES2 Direct Discharge
ERC 2
CS 3 Formulation of metal surface treatment pre-formulations ES3 Marine Discharge
ERC 2
Worker contributing scenario(s):
CS 4 Raw material handling PROC 26, PROC 8b
CS 5 Formulation of solutions PROC 3, PROC 2
CS 6 Filling of solutions containing <25 % of cobalt dinitrate PROC 8b
CS 7 Cleaning & Maintenance PROC 28
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment.
9.6.1. Env CS 1: Formulation of metal surface treatment pre-formulations ES1 STP Discharge (ERC 2)
9.6.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.025 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 4 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 160 days/year The selected number of production days per year is the median value based on data from 8 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use
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and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 200
9.6.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.55. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.125 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T)
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 2.5E-3 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.6.1.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.56. Exposure concentrations and risks for the environment and man via the environment
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Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.18E-4 mg/L RCR = 0.352
Sediment (freshwater) Local PEC: 8.81 mg/kg dw Clocal: 4.55 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.164
Sewage Treatment Plant Local PEC: 0.037 mg/L RCR = 0.101
Agricultural soil Local PEC: 1.292 mg/kg dw RCR = 0.119
Man via environment - Inhalation
Concentration in air: 3.05E-7 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.6.2. Env CS 2: Formulation of metal surface treatment pre-formulations ES2 Direct Discharge (ERC 2)
9.6.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.025 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 4 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 160 days/year The selected number of production days per year is the median value based on data from 8 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds
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waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 300
9.6.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.57. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.125 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T)
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 2.5E-3 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.6.2.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.58. Exposure concentrations and risks for the environment and man via the environment
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Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.32E-4 mg/L RCR = 0.373
Sediment (freshwater) Local PEC: 9.32 mg/kg dw Clocal: 5.06 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.173
Agricultural soil Local PEC: 0.239 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 3.05E-7 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.6.3. Env CS 3: Formulation of metal surface treatment pre-formulations ES3 Marine Discharge (ERC 2)
9.6.3.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.025 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 4 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 160 days/year The selected number of production days per year is the median value based on data from 8 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste.
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Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Marine water only
• Dilution factor to marine water: <= 100
9.6.3.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.59. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.125 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T)
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 2.5E-3 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.6.3.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.60. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.285 µg/L RCR = 0.121
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Protection target Exposure concentration Risk quantification
Clocal: 0.27 µg/L (estimated by Clocal calculation with Kp susp. matter marine (logKp = 4.94))
Sediment (marine water) Local PEC: 38.02 mg/kg dw Clocal: 23.32 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.545
Agricultural soil Local PEC: 0.239 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 3.05E-7 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.6.4. Worker CS 4: Raw material handling (PROC 26, PROC 8b)
Task(s) covered with this contributing scenario: Opening of containers / dosing, dissolution, immediate removal of wet splashes.
9.6.4.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
• Additional physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 15 min Monitoring data
• Shifts per year: <= 57 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%]
Monitoring data
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Method
High efficiency
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.6.4.2. Exposure and risks for workers
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The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.61. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.02 µg/m³ (Measured data: Monitoring data) RCR < 0.01
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.6.5. Worker CS 5: Formulation of solutions (PROC 3, PROC 2)
Task(s) covered with this contributing scenario: Dissolution.
9.6.5.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 52 min Monitoring data
• Shifts per year: <= 59 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
• Level of containment: Closed process Closed pipe system, closed reaction vessels
Monitoring data
• Level of automation: Semi-automated process Monitoring data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency Vapour extraction units in the tank
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the
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Method
conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.6.5.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.62. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 1.4 µg/m³ (Measured data: Monitoring data) RCR = 0.011
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance
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Inhalation exposure, long term concentration: Number of measured data points: 9 ; GSD: 1.9
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.6.6. Worker CS 6: Filling of solutions containing <25 % of cobalt dinitrate (PROC 8b)
Task(s) covered with this contributing scenario: Filling of formulated solutions, immediate removal of wet splashes.
9.6.6.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential: Very low Only the highest emission potential (EP) of the substance in this process is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel or if the actual process temperature or the level of abrasion is lower) are thus automatically covered in this assessment.
Monitoring data
• Content in preparation: 5 - 25 % [Effectiveness Inhalation: 40%, Dermal: 40%] Monitoring data
• Physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 74 min Monitoring data
• Shifts per year: <= 57 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried
Monitoring data
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Method
splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.6.6.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.63. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.95 µg/m³ (Measured data: Monitoring data) RCR < 0.01
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.6.7. Worker CS 7: Cleaning & Maintenance (PROC 28)
Task(s) covered with this contributing scenario: Manual cleaning, repair and maintenance operations, removal of residuals from e.g. filters/overspill or as waste.
9.6.7.1. Conditions of use
Method
Product (article) characteristics
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Method
• Maximum emission potential of the substance: High Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 24 min Monitoring data
• Shifts per year: <= 53 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
• Process pressure: Ambient Monitoring data
• Additional operational conditions for cleaning and maintenance: Maintenance and repair work only at machinery/systems which are not in operation. Minor cleaning tasks may be conducted under operation.
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces.
Cobalt dinitrate
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Method
Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.6.7.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.64. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 2.6 µg/m³ (Measured data: Monitoring data) RCR = 0.021
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 9 ; GSD: 2.66
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.7. Exposure scenario 7: Use at industrial sites - Passivation processes in surface treatment Market sector: Use in surface treatment Product category used: PC 14: Metal surface treatment products Sector of use: SU 15: Manufacture of fabricated metal products, except machinery and equipment
Environment contributing scenario(s):
CS 1 Passivation processes in surface treatment ES1 STP Discharge
ERC 5
CS 2 Passivation processes in surface treatment ES2 Direct Discharge
ERC 5
CS 3 Passivation processes in surface treatment ES3 Marine Discharge
ERC 5
Worker contributing scenario(s):
CS 4 Raw material handling (solid input materials) PROC 5, PROC 1; PROC 2; PROC 8b
CS 5 Raw material handling (exclusively aqueous solutions as input materials)
PROC 4, PROC 9
CS 6 Passivation PROC 13
CS 7 Finishing of passivated articles PROC 21
CS 8 Cleaning & Maintenance PROC 28
Subsequent service life exposure scenario(s): ES10: Service life (worker at industrial site) - Industrial handling of surface treated articles (passivated/plated) ES11: Service life (professional worker) - Professional handling of surface treated articles (passivated/plated)
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment. It is noted that the substance is chemically transformed into another substance during this use. Consequently, exposure can no longer occur to the registered substance. Please refer to information on safe use for the handling of the individual manufactured substances for process steps commencing the chemical transformation step.
9.7.1. Env CS 1: Passivation processes in surface treatment ES1 STP Discharge (ERC 5)
9.7.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.025 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 4 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 160 days/year The selected number of production days per year is the median value based on data from 8 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters,
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Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 200
9.7.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.65. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.125 kg/day Explanation: Eurométaux, 2012, version 2.1
Air Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.2% Release factor after on site RMM: 0.2% Local release rate: 0.05 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
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9.7.1.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.66. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.18E-4 mg/L RCR = 0.352
Sediment (freshwater) Local PEC: 8.81 mg/kg dw Clocal: 4.55 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
RCR = 0.164
Sewage Treatment Plant Local PEC: 0.037 mg/L RCR = 0.101
Agricultural soil Local PEC: 1.294 mg/kg dw RCR = 0.119
Man via environment - Inhalation
Concentration in air: 6.09E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.7.2. Env CS 2: Passivation processes in surface treatment ES2 Direct Discharge (ERC 5)
9.7.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.025 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 4 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 160 days/year The selected number of production days per year is the median value based on data from 8 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
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Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Dilution factor to freshwater: <= 300
9.7.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.67. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.125 kg/day Explanation: Eurométaux, 2012, version 2.1
Air Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.2% Release factor after on site RMM: 0.2% Local release rate: 0.05 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.7.2.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.68. Exposure concentrations and risks for the environment and man via the environment
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Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.32E-4 mg/L RCR = 0.373
Sediment (freshwater) Local PEC: 9.32 mg/kg dw Clocal: 5.06 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
RCR = 0.173
Agricultural soil Local PEC: 0.242 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 6.09E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.7.3. Env CS 3: Passivation processes in surface treatment ES3 Marine Discharge (ERC 5)
9.7.3.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.025 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 4 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 160 days/year The selected number of production days per year is the median value based on data from 8 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste.
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Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Marine water only
• Dilution factor to marine water: <= 100
9.7.3.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.69. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.125 kg/day Explanation: Eurométaux, 2012, version 2.1
Air Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.2% Release factor after on site RMM: 0.2% Local release rate: 0.05 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.7.3.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.70. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.286 µg/L Clocal: 0.271 µg/L (estimated by Clocal calculation with Kp susp. matter marine (logKp = 4.94))
RCR = 0.121
Sediment (marine water) Local PEC: 38.02 mg/kg dw RCR = 0.545
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Protection target Exposure concentration Risk quantification
Clocal: 23.32 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
Agricultural soil Local PEC: 0.242 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 6.09E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.7.4. Worker CS 4: Raw material handling (solid input materials) (PROC 5, PROC 1; PROC 2; PROC 8b)
Task(s) covered with this contributing scenario: Mixing, loading/unloading, weighing, immediate removal of wet splashes, dissolution.
9.7.4.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 10 min Monitoring data
• Shifts per year: <= 4 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency
Monitoring data
• Process temperature: Ambient Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous
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Method
supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.7.4.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.71. Exposure concentrations and risks for workers
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Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.01 µg/m³ (Measured data: Monitoring data) RCR < 0.01
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.7.5. Worker CS 5: Raw material handling (exclusively aqueous solutions as input materials) (PROC 4, PROC 9)
Task(s) covered with this contributing scenario: Mixing, immediate removal of wet splashes, loading/unloading, weighing.
9.7.5.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Content in preparation: 5 - 25 % [Effectiveness Inhalation: 40%, Dermal: 40%] Monitoring data
• Physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 30 min Monitoring data
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general,
Monitoring data
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Method
inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.7.5.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.72. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.8 µg/m³ (Measured data: Monitoring data) RCR < 0.01
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 9 ; GSD: 1.9
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.7.6. Worker CS 6: Passivation (PROC 13)
Task(s) covered with this contributing scenario: Passivation, immediate removal of wet splashes. It is noted that the substance is used as raw material in the treatment of article surfaces. During treatment, the substance is completely transformed into cobalt and deposited as such on the
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respective article surface.
9.7.6.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential: Very low Only the highest emission potential (EP) of the substance in this process is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel or if the actual process temperature or the level of abrasion is lower) are thus automatically covered in this assessment.
MEASE 1.02.01
• Content in preparation: 1 - 5 % [Effectiveness Inhalation: 80%, Dermal: 80%] MEASE 1.02.01
• Physical form of substance: Aqueous solution MEASE 1.02.01
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 35 min MEASE 1.02.01
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
MEASE 1.02.01
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
MEASE 1.02.01
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the
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emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.7.6.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.73. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.1 µg/m³ (MEASE 1.02.01) RCR < 0.01
Remarks on exposure data from external estimation tools:
MEASE 1.02.01: Explanation: Duration of exposure was not reflected in the exposure estimate by using the assessment tool but instead a linear interpolation was applied to the full-shift estimate as derived by the tool.
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.7.7. Worker CS 7: Finishing of passivated articles (PROC 21)
Task(s) covered with this contributing scenario: Packaging and further handling of passivated articles. It is noted that the substance is used as raw material in the treatment of article surfaces. During treatment, the substance is completely transformed into cobalt and deposited as such on the respective article surface.
9.7.7.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Massive object Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 150 min Monitoring data
• Shifts per year: <= 240 Shifts/year Monitoring data
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Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.7.7.2. Exposure and risks for workers
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The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.74. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 2.7 µg/m³ (Measured data: Monitoring data) RCR = 0.022
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1.62
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.7.8. Worker CS 8: Cleaning & Maintenance (PROC 28)
Task(s) covered with this contributing scenario: Manual cleaning, repair and maintenance operations, removal of residuals from e.g. filters/overspill or as waste.
9.7.8.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: High Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 240 min Monitoring data
• Shifts per year: <= 2 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
• Process pressure: Ambient Monitoring data
• Additional operational conditions for cleaning and maintenance: Maintenance and repair work only at machinery/systems which are not in operation. Minor cleaning tasks may be conducted under operation.
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as
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appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.7.8.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.75. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 26.1 µg/m³ (Measured data: Monitoring data) RCR = 0.21
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 9 ; GSD: 2.66
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Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.8. Exposure scenario 8: Use at industrial sites - Passivation processes in surface treatment at large industrial sites with continuous processes Market sector: Use in surface treatment Product category used: PC 14: Metal surface treatment products Sector of use: SU 15: Manufacture of fabricated metal products, except machinery and equipment
Environment contributing scenario(s):
CS 1 Passivation processes in surface treatment at large industrial sites with continuous processes ES1 STP Discharge
ERC 5
CS 2 Passivation processes in surface treatment at large industrial sites with continuous processes ES2 Direct Discharge
ERC 5
CS 3 Passivation processes in surface treatment at large industrial sites with continuous processes ES3 Marine Discharge
ERC 5
Worker contributing scenario(s):
CS 4 Raw material handling (exclusively aqueous solutions as input materials)
PROC 4, PROC 9
CS 5 Passivation PROC 2, PROC 13
CS 6 Finishing of passivated articles PROC 21
Subsequent service life exposure scenario(s): ES10: Service life (worker at industrial site) - Industrial handling of surface treated articles (passivated/plated) ES11: Service life (professional worker) - Professional handling of surface treated articles (passivated/plated)
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment. It is noted that the substance is chemically transformed into another substance during this use. Consequently, exposure can no longer occur to the registered substance. Please refer to information on safe use for the handling of the individual manufactured substances for process steps commencing the chemical transformation step.
9.8.1. Env CS 1: Passivation processes in surface treatment at large industrial sites with continuous processes ES1 STP Discharge (ERC 5)
9.8.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.025 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 4 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 160 days/year The selected number of production days per year is the median value based on data from 8 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air:
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One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 200
9.8.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.76. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.125 kg/day Explanation: Eurométaux, 2012, version 2.1
Air Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.2% Release factor after on site RMM: 0.2% Local release rate: 0.05 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
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Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.8.1.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.77. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.18E-4 mg/L RCR = 0.352
Sediment (freshwater) Local PEC: 8.81 mg/kg dw Clocal: 4.55 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
RCR = 0.164
Sewage Treatment Plant Local PEC: 0.037 mg/L RCR = 0.101
Agricultural soil Local PEC: 1.294 mg/kg dw RCR = 0.119
Man via environment - Inhalation
Concentration in air: 6.09E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.8.2. Env CS 2: Passivation processes in surface treatment at large industrial sites with continuous processes ES2 Direct Discharge (ERC 5)
9.8.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.025 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 4 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 160 days/year The selected number of production days per year is the median value based on data from 8 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
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• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Dilution factor to freshwater: <= 300
9.8.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.78. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.125 kg/day Explanation: Eurométaux, 2012, version 2.1
Air Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.2% Release factor after on site RMM: 0.2% Local release rate: 0.05 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.8.2.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
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Table 9.79. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.32E-4 mg/L RCR = 0.373
Sediment (freshwater) Local PEC: 9.32 mg/kg dw Clocal: 5.06 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
RCR = 0.173
Agricultural soil Local PEC: 0.242 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 6.09E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.8.3. Env CS 3: Passivation processes in surface treatment at large industrial sites with continuous processes ES3 Marine Discharge
(ERC 5)
9.8.3.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.025 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 4 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 160 days/year The selected number of production days per year is the median value based on data from 8 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
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• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Marine water only
• Dilution factor to marine water: <= 100
9.8.3.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.80. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.125 kg/day Explanation: Eurométaux, 2012, version 2.1
Air Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.2% Release factor after on site RMM: 0.2% Local release rate: 0.05 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.8.3.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.81. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.286 µg/L Clocal: 0.271 µg/L (estimated by Clocal
RCR = 0.121
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Protection target Exposure concentration Risk quantification
calculation with Kp susp. matter marine (logKp = 4.94))
Sediment (marine water) Local PEC: 38.02 mg/kg dw Clocal: 23.32 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
RCR = 0.545
Agricultural soil Local PEC: 0.242 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 6.09E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.8.4. Worker CS 4: Raw material handling (exclusively aqueous solutions as input materials) (PROC 4, PROC 9)
Task(s) covered with this contributing scenario: Mixing, immediate removal of wet splashes, loading/unloading, weighing, immediate removal of wet splashes.
9.8.4.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Content in preparation: 5 - 25 % [Effectiveness Inhalation: 40%, Dermal: 40%] Analogous data
• Physical form of substance: Aqueous solution Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 15 min Analogous data
• Shifts per year: <= 12 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Level of automation: Fully automated process Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required
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Method
Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.8.4.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.82. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.4 µg/m³ (Measured data: Analogous data) RCR < 0.01
Remarks on measured exposure:
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Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 9 ; GSD: 1.9
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.8.5. Worker CS 5: Passivation (PROC 2, PROC 13)
Task(s) covered with this contributing scenario: Control walks, supervision, adjusting machinery. It is noted that the substance is used as raw material in the treatment of article surfaces. During treatment, the substance is completely transformed into cobalt and deposited as such on the respective article surface.
9.8.5.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential: Very low Only the highest emission potential (EP) of the substance in this process is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel or if the actual process temperature or the level of abrasion is lower) are thus automatically covered in this assessment.
MEASE 1.02.01
• Content in preparation: 1 - 5 % [Effectiveness Inhalation: 80%, Dermal: 80%] MEASE 1.02.01
• Physical form of substance: Aqueous solution MEASE 1.02.01
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 15 min MEASE 1.02.01
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
MEASE 1.02.01
Technical and organisational conditions and measures
• Level of containment: Closed process MEASE 1.02.01
• Level of automation: Fully automated process MEASE 1.02.01
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency
MEASE 1.02.01
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the
MEASE 1.02.01
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Method
substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.8.5.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.83. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.03 µg/m³ (MEASE 1.02.01) RCR < 0.01
Remarks on exposure data from external estimation tools:
MEASE 1.02.01: Explanation: Duration of exposure was not reflected in the exposure estimate by using the assessment tool but instead a linear interpolation was applied to the full-shift estimate as derived by the tool.
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.8.6. Worker CS 6: Finishing of passivated articles (PROC 21)
Task(s) covered with this contributing scenario: Etching, polishing and handling of passivated articles. It is noted that the substance is used as raw material in the treatment of article surfaces. During treatment, the substance is completely transformed into cobalt and deposited as such on the respective article surface.
9.8.6.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Massive object Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 240 min Monitoring data
• Shifts per year: <= 60 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Level of automation: Fully automated process Monitoring data
• Process temperature: Ambient Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
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Method
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.8.6.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.84. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 4.3 µg/m³ (Measured data: Monitoring data) RCR = 0.035
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1.62
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.9. Exposure scenario 9: Use at industrial sites - Plating processes in surface treatment Market sector: Use in surface treatment Product category used: PC 14: Metal surface treatment products Sector of use: SU 15: Manufacture of fabricated metal products, except machinery and equipment
Environment contributing scenario(s):
CS 1 Plating processes in surface treatment ES1 STP Discharge ERC 5
CS 2 Plating processes in surface treatment ES2 Direct Discharge
ERC 5
CS 3 Plating processes in surface treatment ES3 Marine Discharge
ERC 5
Worker contributing scenario(s):
CS 4 Raw material handling (solid input materials) PROC 5, PROC 1; PROC 2; PROC 8b
CS 5 Raw material handling (exclusively aqueous solutions as input materials)
PROC 4, PROC 9
CS 6 Plating PROC 13
CS 7 Manual brush plating PROC 10
CS 8 Finishing of coated/plated articles PROC 21
CS 9 Cleaning & Maintenance PROC 28
Subsequent service life exposure scenario(s): ES10: Service life (worker at industrial site) - Industrial handling of surface treated articles (passivated/plated) ES11: Service life (professional worker) - Professional handling of surface treated articles (passivated/plated)
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment. It is noted that the substance is chemically transformed into another substance during this use. Consequently, exposure can no longer occur to the registered substance. Please refer to information on safe use for the handling of the individual manufactured substances for process steps commencing the chemical transformation step.
9.9.1. Env CS 1: Plating processes in surface treatment ES1 STP Discharge (ERC 5)
9.9.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.025 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 4 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 160 days/year The selected number of production days per year is the median value based on data from 8 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters,
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Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 200
9.9.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.85. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.125 kg/day Explanation: Eurométaux, 2012, version 2.1
Air Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.2% Release factor after on site RMM: 0.2% Local release rate: 0.05 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
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9.9.1.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.86. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.18E-4 mg/L RCR = 0.352
Sediment (freshwater) Local PEC: 8.81 mg/kg dw Clocal: 4.55 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
RCR = 0.164
Sewage Treatment Plant Local PEC: 0.037 mg/L RCR = 0.101
Agricultural soil Local PEC: 1.294 mg/kg dw RCR = 0.119
Man via environment - Inhalation
Concentration in air: 6.09E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.9.2. Env CS 2: Plating processes in surface treatment ES2 Direct Discharge (ERC 5)
9.9.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.025 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 4 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 160 days/year The selected number of production days per year is the median value based on data from 8 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
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Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Dilution factor to freshwater: <= 300
9.9.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.87. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.125 kg/day Explanation: Eurométaux, 2012, version 2.1
Air Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.2% Release factor after on site RMM: 0.2% Local release rate: 0.05 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.9.2.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.88. Exposure concentrations and risks for the environment and man via the environment
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Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.32E-4 mg/L RCR = 0.373
Sediment (freshwater) Local PEC: 9.32 mg/kg dw Clocal: 5.06 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
RCR = 0.173
Agricultural soil Local PEC: 0.242 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 6.09E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.9.3. Env CS 3: Plating processes in surface treatment ES3 Marine Discharge (ERC 5)
9.9.3.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.025 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 4 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 160 days/year The selected number of production days per year is the median value based on data from 8 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste.
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Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Marine water only
• Dilution factor to marine water: <= 100
9.9.3.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.89. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.125 kg/day Explanation: Eurométaux, 2012, version 2.1
Air Estimated release factor (SpERC Metallic coating)
Release factor before on site RMM: 0.2% Release factor after on site RMM: 0.2% Local release rate: 0.05 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.9.3.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.90. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.286 µg/L Clocal: 0.271 µg/L (estimated by Clocal calculation with Kp susp. matter marine (logKp = 4.94))
RCR = 0.121
Sediment (marine water) Local PEC: 38.02 mg/kg dw RCR = 0.545
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Protection target Exposure concentration Risk quantification
Clocal: 23.32 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
Agricultural soil Local PEC: 0.242 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 6.09E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.9.4. Worker CS 4: Raw material handling (solid input materials) (PROC 5, PROC 1; PROC 2; PROC 8b)
Task(s) covered with this contributing scenario: Mixing, loading/unloading, weighing, dissolution.
9.9.4.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Analogous data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Analogous data
• Physical form of substance: Solid, powder / dust Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 10 min Analogous data
• Shifts per year: <= 4 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency
Analogous data
• Process temperature: Ambient Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%]
Analogous data
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APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.9.4.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.91. Exposure concentrations and risks for workers
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Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 1 µg/m³ (Measured data: Analogous data) RCR < 0.01
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 147 ; GSD: 4.55
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.9.5. Worker CS 5: Raw material handling (exclusively aqueous solutions as input materials) (PROC 4, PROC 9)
Task(s) covered with this contributing scenario: Mixing, immediate removal of wet splashes, loading/unloading, weighing.
9.9.5.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 33 min Monitoring data
• Shifts per year: <= 195 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable
Monitoring data
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cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.9.5.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.92. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.9 µg/m³ (Measured data: Monitoring data) RCR < 0.01
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 9 ; GSD: 1.9
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.9.6. Worker CS 6: Plating (PROC 13)
Task(s) covered with this contributing scenario: Plating. It is noted that the substance is used as raw material in the treatment of article surfaces. During
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treatment, the substance is completely transformed into cobalt metal and deposited as such on the respective article surface.
9.9.6.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 240 min Monitoring data
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Level of containment: Closed process Closed pipe system, closed reaction vessels
Monitoring data
• Level of automation: Semi-automated process Monitoring data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency Vapour extraction units in the tank
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as
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appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.9.6.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.93. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 8.6 µg/m³ (Measured data: Monitoring data) RCR = 0.069
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 60 ; GSD: 2.82
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.9.7. Worker CS 7: Manual brush plating (PROC 10)
Task(s) covered with this contributing scenario: Manual brush plating, immediate removal of wet splashes. It is noted that the substance is used as raw material in the treatment of article surfaces. During treatment, the substance is completely transformed into cobalt metal and deposited as such on the respective article surface.
9.9.7.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential: Low (vapour pressure based) Only the highest emission potential (EP) of the substance in this process is
MEASE 1.02.01
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reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel or if the actual process temperature or the level of abrasion is lower) are thus automatically covered in this assessment.
• Content in preparation: 1 - 5 % [Effectiveness Inhalation: 80%, Dermal: 80%] MEASE 1.02.01
• Physical form of substance: Liquid Due to the high current applied (90 A - 195 A) during manual brush plating, the more precise term “aqueous solution” for describing the used mixture was replaced by “liquid” in order to highlight the increased emission potential. In the exposure assessment with MEASE, a “low fugacity” was thus assumed by entering a hypothetical vapour pressure of below 500 Pa which is far above the vapour pressure of Co in aqueous solution. The resulting exposure assessment is therefore assumed to be sufficiently precautionary.
MEASE 1.02.01
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 360 min MEASE 1.02.01
• Shifts per year: <= 24 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
MEASE 1.02.01
Technical and organisational conditions and measures
• Generic local exhaust ventilation: Lower confidence limit (industrial use) [Effectiveness Inhalation: 78%] Standard efficiency
MEASE 1.02.01
Conditions and measures related to personal protection, hygiene and health evaluation
• Respiratory protective equipment (RPE): RPE with minimum APF = 20 [Effectiveness Inhalation: 95%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P3 with mask according to EN 140, EN 1827 or filtering half mask (FF P3) according to EN 149 or combination of P2 filter with face piece according to EN 12941 or EN 12942 or any RPE providing higher APFs according to EN 529 is required.
MEASE 1.02.01
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in
MEASE 1.02.01
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the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.9.7.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.94. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 16.5 µg/m³ (MEASE 1.02.01) RCR = 0.133
Remarks on exposure data from external estimation tools:
MEASE 1.02.01: Explanation: Duration of exposure was not reflected in the exposure estimate by using the assessment tool but instead a linear interpolation was applied to the full-shift estimate as derived by the tool.
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.9.8. Worker CS 8: Finishing of coated/plated articles (PROC 21)
Task(s) covered with this contributing scenario: Etching, polishing and handling of coated/plated articles. It is noted that the substance is used as raw material in the treatment of article surfaces. During treatment, the substance is completely transformed into cobalt metal and deposited as such on the respective article surface.
9.9.8.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if
Monitoring data
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materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Massive object Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 165 min Monitoring data
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face
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protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.9.8.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.95. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 3 µg/m³ (Measured data: Monitoring data) RCR = 0.024
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1.62
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.9.9. Worker CS 9: Cleaning & Maintenance (PROC 28)
Task(s) covered with this contributing scenario: Manual cleaning, repair and maintenance operations; Removal of residuals from e.g. filters/overspill or as waste.
9.9.9.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: High Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 240 min Monitoring data
• Shifts per year: <= 121 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
• Process pressure: Ambient Monitoring data
• Additional operational conditions for cleaning and maintenance: Maintenance and repair work only at machinery/systems which are not in operation. Minor
Monitoring data
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Method
cleaning tasks may be conducted under operation.
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.9.9.2. Exposure and risks for workers
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The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.96. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 26.1 µg/m³ (Measured data: Monitoring data) RCR = 0.21
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 9 ; GSD: 2.66
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.10. Exposure scenario 10: Service life (worker at industrial site) - Industrial handling of surface treated articles (passivated/plated) Market sector: Use in surface treatment Article categories: AC 2: Machinery, mechanical appliances, electrical/electronic articles AC 7: Metal articles
Environment contributing scenario(s):
CS 1 Handling of surface treated articles (passivated/plated) ERC 12a
Worker contributing scenario(s):
CS 2 Handling of articles PROC 21
Exposure scenario(s) of the uses leading to the inclusion of the substance into the article(s): ES7: Use at industrial sites - Passivation processes in surface treatment ES8: Use at industrial sites - Passivation processes in surface treatment at large industrial sites with continuous processes ES9: Use at industrial sites - Plating processes in surface treatment
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment. It is noted that the substance is used as raw material in the production of surface treated articles. During the production, the substance is completely transformed into another substance. Consequently, exposure can no longer occur to the registered substance.
9.10.1. Env CS 1: Handling of surface treated articles (passivated/plated) (ERC 12a)
9.10.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.5 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 10 tonnes/year
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low risk) Fraction of daily/annual use expected in waste: 60% of all articles, 40% is recycled. (EC, 2010) Appropriate waste codes: 20 01 34, 20 01 40, 20 03 01, 20 03 07, … Suitable Disposal: Waste from end-of-life articles can be disposed of as municipal waste, except when they are separately regulated, like electronic devices, batteries, vehicles, etc. Disposal of wastes is possible via incineration (operated according to Directive 2000/76/EC on the incineration of waste) or landfilling (operated according to Reference Document on the Best available Techniques for Waste Industries of August 2006 and Council Directive 1999/31/EC and Council Decision 19 December 2002). A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.10.1.2. Releases
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The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.97. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 0% Release factor after on site RMM: 0% Local release rate: 0 kg/day Explanation: There are no intended cobalt releases due to service life of surface treated articles, the non-intended releases are negligible and pose no threat to the environment.
Air Estimated release factor Release factor before on site RMM: 0% Release factor after on site RMM: 0% Local release rate: 0 kg/day Explanation: Not relevant
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: Not relevant
Releases to waste
Release factor to external waste: 60 % Fraction of daily/annual use expected in waste: 60% of all articles, 40% is recycled. (EC, 2010). Note that the 60% does not specifically apply to this use but applies to all professional, consumer or service life uses from cobalt. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.10.1.3. Exposure and risks for the environment and man via the environment
No exposure datasets are defined for this environmental contributing scenario.
Risk characterisation
The exposure concentrations and risk characterisation ratios (RCR) for the service life are negligible and pose no threat to the environment. Emission data from municipal STPs have been collected for Belgium (via VMM) and The Netherlands (WATSON database). For Belgium 6 data points are available between 2011 and 2013. Only one data point is above the DL, the effluent concentration of the STP above the DL is 3 µg Co/L. For the Netherlands 272 data points are available between 2005 and 2012. Only 69 data points are above the DL, the median effluent concentration is below the DL and the 90th percentile is 2.69 µg Co/L. These concentrations are a factor 100 below the PNEC for STP of 370 µg Co/L.
9.10.2. Worker CS 2: Handling of articles (PROC 21)
It is noted that the substance is used as raw material in the treatment of article surfaces. During treatment, the substance is completely transformed into cobalt and deposited as such on the respective article surface.
9.10.2.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Analogous data
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Method
• Physical form of substance: Massive object Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Analogous data
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE
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Method
(minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.10.2.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.98. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 2.8 µg/m³ (Measured data: Analogous data) RCR = 0.023
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1.62
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.11. Exposure scenario 11: Service life (professional worker) - Professional handling of surface treated articles (passivated/plated) Market sector: Use in surface treatment Article categories: AC 2: Machinery, mechanical appliances, electrical/electronic articles AC 7: Metal articles
Environment contributing scenario(s):
CS 1 Handling of surface treated articles (passivated/plated) ERC 10a, ERC 11a
Worker contributing scenario(s):
CS 2 Handling of articles PROC 21
Exposure scenario(s) of the uses leading to the inclusion of the substance into the article(s): ES7: Use at industrial sites - Passivation processes in surface treatment ES8: Use at industrial sites - Passivation processes in surface treatment at large industrial sites with continuous processes ES9: Use at industrial sites - Plating processes in surface treatment
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment. It is noted that the substance is used as raw material in the production of surface treated articles. During the production, the substance is completely transformed into another substance. Consequently, exposure can no longer occur to the registered substance.
9.11.1. Env CS 1: Handling of surface treated articles (passivated/plated) (ERC 10a)
9.11.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily local widespread use amount: <= 5.5E-6 tonnes/day The tonnage and further exposure is always expressed in cobalt.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low risk) Fraction of daily/annual use expected in waste: 60% of all articles, 40% is recycled. (EC, 2010) Appropriate waste codes: 20 01 34, 20 01 40, 20 03 01, 20 03 07, … Suitable Disposal: Waste from end-of-life articles can be disposed of as municipal waste, except when they are separately regulated, like electronic devices, batteries, vehicles, etc. Disposal of wastes is possible via incineration (operated according to Directive 2000/76/EC on the incineration of waste) or landfilling (operated according to Reference Document on the Best available Techniques for Waste Industries of August 2006 and Council Directive 1999/31/EC and Council Decision 19 December 2002). A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.11.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.99. Local releases to the environment
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Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 0% Release factor after on site RMM: 0% Local release rate: 0 kg/day Explanation: There are no intended cobalt releases due to service life of surface treated articles, the non-intended releases are negligible and pose no threat to the environment.
Air Estimated release factor Release factor before on site RMM: 0% Release factor after on site RMM: 0% Explanation: Not relevant
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: Not relevant
Releases to waste
Release factor to external waste: 60 % Fraction of daily/annual use expected in waste: 60% of all articles, 40% is recycled. (EC, 2010). Note that the 60% does not specifically apply to this use but applies to all professional, consumer or service life uses from cobalt. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.11.1.3. Exposure and risks for the environment and man via the environment
No exposure datasets are defined for this environmental contributing scenario.
Risk characterisation
The exposure concentrations and risk characterisation ratios (RCR) for the service life are negligible and pose no threat to the environment. Emission data from municipal STPs have been collected for Belgium (via VMM) and The Netherlands (WATSON database). For Belgium 6 data points are available between 2011 and 2013. Only one data point is above the DL, the effluent concentration of the STP above the DL is 3 µg Co/L. For the Netherlands 272 data points are available between 2005 and 2012. Only 69 data points are above the DL, the median effluent concentration is below the DL and the 90th percentile is 2.69 µg Co/L. These concentrations are a factor 100 below the PNEC for STP of 370 µg Co/L.
9.11.2. Worker CS 2: Handling of articles (PROC 21)
It is noted that the substance is used as raw material in the treatment of article surfaces. During treatment, the substance is completely transformed into cobalt and deposited as such on the respective article surface.
9.11.2.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Analogous data
• Physical form of substance: Massive object Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Analogous data
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Method
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
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9.11.2.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.100. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 2.8 µg/m³ (Measured data: Analogous data) RCR = 0.023
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1.62
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.12. Exposure scenario 12: Formulation or re-packing - Formulation for water treatment chemicals, oxygen scavengers, corrosion inhibitors Market sector: Water treatment chemicals, oxygen scavengers and corrosion inhibitors Product category formulated: PC 20: Products such as ph-regulators, flocculants, precipitants, neutralization agents; PC 21: Laboratory Chemicals; PC 37: Water treatment chemicals
Environment contributing scenario(s):
CS 1 Formulation for water treatment chemicals, oxygen scavengers, corrosion inhibitors ES1 STP Discharge
ERC 2
CS 2 Formulation for water treatment chemicals, oxygen scavengers, corrosion inhibitors ES2 Direct Discharge
ERC 2
CS 3 Formulation for water treatment chemicals, oxygen scavengers, corrosion inhibitors ES3 Marine Discharge
ERC 2
Worker contributing scenario(s):
CS 4 Formulation PROC 26, PROC 15; PROC 2; PROC 4; PROC 5; PROC 8b; PROC 9
CS 5 Cleaning & Maintenance PROC 28
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment.
9.12.1. Env CS 1: Formulation for water treatment chemicals, oxygen scavengers, corrosion inhibitors ES1 STP Discharge (ERC 2)
9.12.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 6.8E-3 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 1.5 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 220 days/year The selected number of production days per year is the median value based on data from 1 company.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
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• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 100
9.12.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.101. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.034 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T)
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.8E-4 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.12.1.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
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Table 9.102. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 1.64E-4 mg/L RCR = 0.265
Sediment (freshwater) Local PEC: 6.74 mg/kg dw Clocal: 2.48 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.125
Sewage Treatment Plant Local PEC: 0.01 mg/L RCR = 0.028
Agricultural soil Local PEC: 0.525 mg/kg dw RCR = 0.048
Man via environment - Inhalation
Concentration in air: 1.14E-7 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.12.2. Env CS 2: Formulation for water treatment chemicals, oxygen scavengers, corrosion inhibitors ES2 Direct Discharge (ERC 2)
9.12.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 6.8E-3 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 1.5 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 220 days/year The selected number of production days per year is the median value based on data from 1 company.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
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Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 100
9.12.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.103. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.034 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T)
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.8E-4 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.12.2.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
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Table 9.104. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.07E-4 mg/L RCR = 0.334
Sediment (freshwater) Local PEC: 8.4 mg/kg dw Clocal: 4.14 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.156
Agricultural soil Local PEC: 0.239 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.14E-7 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.12.3. Env CS 3: Formulation for water treatment chemicals, oxygen scavengers, corrosion inhibitors ES3 Marine Discharge
(ERC 2)
9.12.3.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 6.8E-3 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 1.5 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 220 days/year The selected number of production days per year is the median value based on data from 1 company.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
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• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Marine water only
• Dilution factor to marine water: <= 100
9.12.3.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.105. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.034 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T)
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.8E-4 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.12.3.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.106. Exposure concentrations and risks for the environment and man via the
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environment
Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.089 µg/L Clocal: 0.074 µg/L (estimated by Clocal calculation with Kp susp. matter marine (logKp = 4.94))
RCR = 0.038
Sediment (marine water) Local PEC: 21.06 mg/kg dw Clocal: 6.36 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.302
Agricultural soil Local PEC: 0.239 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.14E-7 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.12.4. Worker CS 4: Formulation (PROC 26, PROC 15; PROC 2; PROC 4; PROC 5; PROC 8b; PROC 9)
Task(s) covered with this contributing scenario: Opening of containers / dosing, loading/unloading, weighing, re-packaging, mixing, dissolution, sampling, immediate removal of wet splashes
9.12.4.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Analogous data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Analogous data
• Physical form of substance: Solid, powder / dust Analogous data
• Additional physical form of substance: Aqueous solution Analogous data
• Additional physical form of substance: Solid, crystal Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Analogous data
• Shifts per year: <= 24 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
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Method
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency
Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Analogous data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission
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Method
source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.12.4.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.107. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 46.2 µg/m³ (Measured data: Analogous data) RCR = 0.372
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 147 ; GSD: 4.55
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.12.5. Worker CS 5: Cleaning & Maintenance (PROC 28)
Task(s) covered with this contributing scenario: Manual cleaning, repair and maintenance operations, removal of residuals from e.g. filters/overspill or as waste.
9.12.5.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: High Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Physical form of substance: Solid, powder / dust Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Analogous data
• Shifts per year: <= 48 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
• Process pressure: Ambient Analogous data
• Additional operational conditions for cleaning and maintenance: Maintenance and repair work only at machinery/systems which are not in operation. Minor cleaning tasks may be conducted under operation.
Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any
Analogous data
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Method
combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.12.5.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.108. Exposure concentrations and risks for workers
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Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 33.9 µg/m³ (Measured data: Analogous data) RCR = 0.273
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 187 ; GSD: 4.44
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.13. Exposure scenario 13: Use at industrial sites - Use of water treatment chemicals, oxygen scavengers, corrosion inhibitors Market sector: Water treatment chemicals, oxygen scavengers and corrosion inhibitors Product category used: PC 20: Products such as ph-regulators, flocculants, precipitants, neutralization agents; PC 21: Laboratory Chemicals; PC 37: Water treatment chemicals
Environment contributing scenario(s):
CS 1 Use of water treatment chemicals, oxygen scavengers, corrosion inhibitors ES1 STP Discharge
ERC 6b
CS 2 Use of water treatment chemicals, oxygen scavengers, corrosion inhibitors ES2 Direct Discharge
ERC 6b
CS 3 Use of water treatment chemicals, oxygen scavengers, corrosion inhibitors ES3 Marine Discharge
ERC 6b
Worker contributing scenario(s):
CS 4 Use of formulation PROC 8b, PROC 2
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment.
9.13.1. Env CS 1: Use of water treatment chemicals, oxygen scavengers, corrosion inhibitors ES1 STP Discharge (ERC 6b)
9.13.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 6.8E-3 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 1.5 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 220 days/year The selected number of production days per year is the median value based on data from 1 company.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds
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waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 100
9.13.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.109. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.034 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T)
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.8E-4 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.13.1.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.110. Exposure concentrations and risks for the environment and man via the environment
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Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 1.64E-4 mg/L RCR = 0.265
Sediment (freshwater) Local PEC: 6.74 mg/kg dw Clocal: 2.48 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.125
Sewage Treatment Plant Local PEC: 0.01 mg/L RCR = 0.028
Agricultural soil Local PEC: 0.525 mg/kg dw RCR = 0.048
Man via environment - Inhalation
Concentration in air: 1.14E-7 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.13.2. Env CS 2: Use of water treatment chemicals, oxygen scavengers, corrosion inhibitors ES2 Direct Discharge (ERC 6b)
9.13.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 6.8E-3 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 1.5 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 220 days/year The selected number of production days per year is the median value based on data from 1 company.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds
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waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 100
9.13.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.111. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.034 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T)
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.8E-4 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.13.2.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.112. Exposure concentrations and risks for the environment and man via the environment
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Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.07E-4 mg/L RCR = 0.334
Sediment (freshwater) Local PEC: 8.4 mg/kg dw Clocal: 4.14 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.156
Agricultural soil Local PEC: 0.239 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.14E-7 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.13.3. Env CS 3: Use of water treatment chemicals, oxygen scavengers, corrosion inhibitors ES3 Marine Discharge (ERC 6b)
9.13.3.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 6.8E-3 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 1.5 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 220 days/year The selected number of production days per year is the median value based on data from 1 company.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste.
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Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Marine water only
• Dilution factor to marine water: <= 100
9.13.3.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.113. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.034 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T)
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.8E-4 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.13.3.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.114. Exposure concentrations and risks for the environment and man via the environment
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Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.089 µg/L Clocal: 0.074 µg/L (estimated by Clocal calculation with Kp susp. matter marine (logKp = 4.94))
RCR = 0.038
Sediment (marine water) Local PEC: 21.06 mg/kg dw Clocal: 6.36 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.302
Agricultural soil Local PEC: 0.239 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.14E-7 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.13.4. Worker CS 4: Use of formulation (PROC 8b, PROC 2)
Task(s) covered with this contributing scenario: Use of water treatment chemicals, oxygen scavengers and corrosion inhibitors, immediate removal of wet splashes.
9.13.4.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Analogous data
• Physical form of substance: Aqueous solution Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 15 min Analogous data
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
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Method
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.13.4.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.115. Exposure concentrations and risks for workers
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Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.4 µg/m³ (Measured data: Analogous data) RCR < 0.01
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 9 ; GSD: 1.9
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.14. Exposure scenario 14: Use at industrial sites - Battery production (intermediate use) Market sector: Battery production (intermediate use) Sector of use: SU 16: Manufacture of computer, electronic and optical products, electrical equipment
Environment contributing scenario(s):
CS 1 Battery production (intermediate use) ES1 Direct Discharge ERC 5
CS 2 Battery production (intermediate use) ES2 Marine Discharge
ERC 5
Worker contributing scenario(s):
CS 3 Raw material handling PROC 26, PROC 3; PROC 4; PROC 8b
CS 4 Mix preparation PROC 5, PROC 3
CS 5 Further processing PROC 13, PROC 3; PROC 4; PROC 5; PROC 6; PROC 9
CS 6 Final processing and handling PROC 14, PROC 21
CS 7 Cleaning & Maintenance PROC 28
Subsequent service life exposure scenario(s): ES15: Service life (worker at industrial site) - Service life of cobalt-containing industrial batteries in industrial settings ES16: Service life (professional worker) - Service life of cobalt-containing portable batteries in professional settings
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment. It is noted that the substance is chemically transformed into another substance during this use. Consequently, exposure can no longer occur to the registered substance. Please refer to information on safe use for the handling of the individual manufactured substances for process steps commencing the chemical transformation step.
9.14.1. Env CS 1: Battery production (intermediate use) ES1 Direct Discharge (ERC 5)
9.14.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.088 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 28 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 319 days/year The selected number of production days per year is the median value based on data from 9 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
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• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 513 m3/day The selected effluent discharge rate is the median value based on data from 2 companies.
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 100
9.14.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.116. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 0.011% Release factor after on site RMM: 0.011% Local release rate: 9.57E-3 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 2 companies.
Air Estimated release factor Release factor before on site RMM: 1.17E-3% Release factor after on site RMM: 1.17E-3% Local release rate: 1.03E-3 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 1 companies.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
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Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.14.1.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.117. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.18E-4 mg/L RCR = 0.351
Sediment (freshwater) Local PEC: 8.78 mg/kg dw Clocal: 4.52 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
RCR = 0.163
Agricultural soil Local PEC: 0.239 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 2.5E-7 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.14.2. Env CS 2: Battery production (intermediate use) ES2 Marine Discharge (ERC 5)
9.14.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.088 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 28 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 319 days/year The selected number of production days per year is the median value based on data from 9 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
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Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 513 m3/day The selected effluent discharge rate is the median value based on data from 2 companies.
• Discharge to: Marine water only
• Dilution factor to marine water: <= 100
9.14.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.118. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 0.011% Release factor after on site RMM: 0.011% Local release rate: 9.57E-3 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 2 companies.
Air Estimated release factor Release factor before on site RMM: 1.17E-3% Release factor after on site RMM: 1.17E-3% Local release rate: 1.03E-3 kg/day Explanation: This release factor is based on reported emissions after on-site treatment. The selected value is the 50th percentile of 1 companies.
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.14.2.3. Exposure and risks for the environment and man via the environment
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The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.119. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.095 µg/L Clocal: 0.08 µg/L (estimated by Clocal calculation with Kp susp. matter marine (logKp = 4.94))
RCR = 0.04
Sediment (marine water) Local PEC: 21.65 mg/kg dw Clocal: 6.95 mg/kg dw (estimated by PEC sediment calculation method for metals (local PEC = Clocal,sed + PECreg,sed))
RCR = 0.31
Agricultural soil Local PEC: 0.239 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 2.5E-7 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.14.3. Worker CS 3: Raw material handling (PROC 26, PROC 3; PROC 4; PROC 8b)
Task(s) covered with this contributing scenario: Powder handling, weighing, immediate removal of wet splashes.
9.14.3.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: High Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Analogous data
• Physical form of substance: Solid, powder / dust Analogous data
• Additional physical form of substance: Aqueous solution Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 30 min Analogous data
• Shifts per year: <= 225 Shifts/year Typical number of shifts per year during which this task is conducted
Analogous data
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Method
considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required. FFP2 mask during powder handling.
Analogous data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission
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Method
source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.14.3.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.120. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 3.3 µg/m³ (Measured data: Analogous data) RCR = 0.027
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 65 ; GSD: 6.19
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.14.4. Worker CS 4: Mix preparation (PROC 5, PROC 3)
Task(s) covered with this contributing scenario: Metal leaching, mixing. It is noted that the substance is used as an intermediate so that the substance is chemically transformed into another substance.
9.14.4.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Analogous data
• Physical form of substance: Aqueous solution Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 160 min Analogous data
• Shifts per year: <= 225 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
• Level of containment: Closed reaction vessel Analogous data
• Level of automation: Semi-automated process Analogous data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency
Analogous data
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Method
Vapour extraction units in the vessel
Conditions and measures related to personal protection, hygiene and health evaluation
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Analogous data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.14.4.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
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Table 9.121. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 2.2 µg/m³ (Measured data: Analogous data) RCR = 0.018
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 77 ; GSD: 3.76
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.14.5. Worker CS 5: Further processing (PROC 13, PROC 3; PROC 4; PROC 5; PROC 6; PROC 9)
Task(s) covered with this contributing scenario: Coating, impregnation, drying, calendaring. It is noted that the substance is used as an intermediate so that the substance is chemically transformed into another substance.
9.14.5.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Low Analogous data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Analogous data
• Physical form of substance: Solid Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Analogous data
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Analogous data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to
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Method
be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.14.5.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.122. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 2.4 µg/m³ (Measured data: Analogous data) RCR = 0.019
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 9 ; GSD: 1.81
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.14.6. Worker CS 6: Final processing and handling (PROC 14,
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PROC 21)
Task(s) covered with this contributing scenario: Pelletizing, tabletting, slitting, battery assembly, packaging. It is noted that the substance is used as an intermediate so that the substance is chemically transformed into another substance.
9.14.6.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Qualitative assessment
• Content in preparation: 5 - 25 % [Effectiveness Inhalation: 40%, Dermal: 40%] Qualitative assessment
• Physical form of substance: Included in closed container Cobalt dihydroxide is in a closed container (battery).
Qualitative assessment
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Qualitative assessment
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Qualitative assessment
Technical and organisational conditions and measures
• Process pressure: Ambient Qualitative assessment
• Process temperature: Ambient Qualitative assessment
9.14.6.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.123. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 1E-3 µg/m³ (Qualitative assessment .) RCR < 0.01
Remarks on exposure data from external estimation tools:
Qualitative assessment .: Explanation: Since batteries are considered as closed containers which cannot lead to exposure under normal condition of use, a qualitative assessment is considered sufficient.
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.14.7. Worker CS 7: Cleaning & Maintenance (PROC 28)
Task(s) covered with this contributing scenario: Manual cleaning, repair and maintenance operations;
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Removal of residuals from e.g. filters/overspill or as waste.
9.14.7.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: High Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Physical form of substance: Solid, powder / dust Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 40 min Analogous data
• Shifts per year: <= 225 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process pressure: Ambient Analogous data
• Process temperature: Ambient Analogous data
• Additional operational conditions for cleaning and maintenance: Maintenance and repair work only at machinery/systems which are not in operation. Minor cleaning tasks may be conducted under operation.
Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Respiratory protective equipment (RPE): RPE with minimum APF = 40 [Effectiveness Inhalation: 97.5%] APF = assigned protection factor according to EN 529. At minimum combination of particle filter class P3 with face piece according to EN 136, EN 12941 or EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Analogous data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried
Analogous data
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Method
splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.14.7.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.124. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 5.4 µg/m³ (Measured data: Analogous data) RCR = 0.043
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 91 ; GSD: 5.96
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.15. Exposure scenario 15: Service life (worker at industrial site) - Service life of cobalt-containing industrial batteries in industrial settings Market sector: Battery production (intermediate use) Article categories: AC 3: Electrical batteries and accumulators
Environment contributing scenario(s):
CS 1 Service life of cobalt-containing industrial batteries in industrial settings
ERC 12a
Worker contributing scenario(s):
CS 2 Handling of closed containers PROC 21
Exposure scenario(s) of the uses leading to the inclusion of the substance into the article(s): ES14: Use at industrial sites - Battery production (intermediate use)
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment. It is noted that the substance is used as raw material in the production of batteries. During the production, the substance is completely transformed into another substance. Consequently, exposure can no longer occur to the registered substance.
9.15.1. Env CS 1: Service life of cobalt-containing industrial batteries in industrial settings (ERC 12a)
9.15.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 5 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 100 tonnes/year
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low risk) Fraction of daily/annual use expected in waste: 60% of all articles, 40% is recycled. (EC, 2010) Appropriate waste codes: 20 01 34, 20 01 40, 20 03 01, 20 03 07, … Suitable Disposal: Waste from end-of-life articles can be disposed of as municipal waste, except when they are separately regulated, like electronic devices, batteries, vehicles, etc. Disposal of wastes is possible via incineration (operated according to Directive 2000/76/EC on the incineration of waste) or landfilling (operated according to Reference Document on the Best available Techniques for Waste Industries of August 2006 and Council Directive 1999/31/EC and Council Decision 19 December 2002). A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.15.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.125. Local releases to the environment
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Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 0% Release factor after on site RMM: 0% Local release rate: 0 kg/day Explanation: There are no intended cobalt releases due to service life of batteries, the non-intended releases are negligible and pose no threat to the environment.
Air Estimated release factor Release factor before on site RMM: 0% Release factor after on site RMM: 0% Local release rate: 0 kg/day Explanation: Not relevant
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: Not relevant
Releases to waste
Release factor to external waste: 60 % Fraction of daily/annual use expected in waste: 60% of all articles, 40% is recycled. (EC, 2010). Note that the 60% does not specifically apply to this use but applies to all professional, consumer or service life uses from cobalt. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.15.1.3. Exposure and risks for the environment and man via the environment
No exposure datasets are defined for this environmental contributing scenario.
Risk characterisation
The exposure concentrations and risk characterisation ratios (RCR) for the service life are negligible and pose no threat to the environment. Emission data from municipal STPs have been collected for Belgium (via VMM) and The Netherlands (WATSON database). For Belgium 6 data points are available between 2011 and 2013. Only one data point is above the DL, the effluent concentration of the STP above the DL is 3 µg Co/L. For the Netherlands 272 data points are available between 2005 and 2012. Only 69 data points are above the DL, the median effluent concentration is below the DL and the 90th percentile is 2.69 µg Co/L. These concentrations are a factor 100 below the PNEC for STP of 370 µg Co/L.
9.15.2. Worker CS 2: Handling of closed containers (PROC 21)
It is noted that the substance is used as an intermediate so that the substance is chemically transformed into another substance.
9.15.2.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Qualitative assessment
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%] The content of the substance in a sealed battery is considered as being not relevant for occupational exposure if used as intended.
Qualitative assessment
• Physical form of substance: Included in closed container Cobalt is in a sealed container (battery).
Qualitative assessment
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Method
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Qualitative assessment
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Qualitative assessment
Technical and organisational conditions and measures
• Process pressure: Ambient Qualitative assessment
• Process temperature: Ambient Qualitative assessment
9.15.2.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.126. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 1E-3 µg/m³ (Qualitative assessment .) RCR < 0.01
Remarks on exposure data from external estimation tools:
Qualitative assessment .: Explanation: Since batteries are considered as closed containers which cannot lead to exposure under normal condition of use, a qualitative assessment is considered sufficient.
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.16. Exposure scenario 16: Service life (professional worker) - Service life of cobalt-containing portable batteries in professional settings Market sector: Battery production (intermediate use) Article categories: AC 3: Electrical batteries and accumulators
Environment contributing scenario(s):
CS 1 Service life of cobalt-containing portable batteries in professional settings
ERC 10a, ERC 11a
Worker contributing scenario(s):
CS 2 Handling of closed containers PROC 21
Exposure scenario(s) of the uses leading to the inclusion of the substance into the article(s): ES14: Use at industrial sites - Battery production (intermediate use)
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment. It is noted that the substance is used as raw material in the production of batteries. During the production, the substance is completely transformed into another substance. Consequently, exposure can no longer occur to the registered substance.
9.16.1. Env CS 1: Service life of cobalt-containing portable batteries in professional settings (ERC 10a)
9.16.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily local widespread use amount: <= 5.5E-5 tonnes/day The tonnage and further exposure is always expressed in cobalt.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low risk) Fraction of daily/annual use expected in waste: 60% of all articles, 40% is recycled. (EC, 2010) Appropriate waste codes: 20 01 34, 20 01 40, 20 03 01, 20 03 07, … Suitable Disposal: Waste from end-of-life articles can be disposed of as municipal waste, except when they are separately regulated, like electronic devices, batteries, vehicles, etc. Disposal of wastes is possible via incineration (operated according to Directive 2000/76/EC on the incineration of waste) or landfilling (operated according to Reference Document on the Best available Techniques for Waste Industries of August 2006 and Council Directive 1999/31/EC and Council Decision 19 December 2002). A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.16.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.127. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 0%
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Release Release estimation method
Explanations
Release factor after on site RMM: 0% Local release rate: 0 kg/day Explanation: There are no intended cobalt releases due to service life of batteries, the non-intended releases are negligible and pose no threat to the environment.
Air Estimated release factor Release factor before on site RMM: 0% Release factor after on site RMM: 0% Explanation: Not relevant
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: Not relevant
Releases to waste
Release factor to external waste: 60 % Fraction of daily/annual use expected in waste: 60% of all articles, 40% is recycled. (EC, 2010). Note that the 60% does not specifically apply to this use but applies to all professional, consumer or service life uses from cobalt. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.16.1.3. Exposure and risks for the environment and man via the environment
No exposure datasets are defined for this environmental contributing scenario.
Risk characterisation
The exposure concentrations and risk characterisation ratios (RCR) for the service life are negligible and pose no threat to the environment. Emission data from municipal STPs have been collected for Belgium (via VMM) and The Netherlands (WATSON database). For Belgium 6 data points are available between 2011 and 2013. Only one data point is above the DL, the effluent concentration of the STP above the DL is 3 µg Co/L. For the Netherlands 272 data points are available between 2005 and 2012. Only 69 data points are above the DL, the median effluent concentration is below the DL and the 90th percentile is 2.69 µg Co/L. These concentrations are a factor 100 below the PNEC for STP of 370 µg Co/L.
9.16.2. Worker CS 2: Handling of closed containers (PROC 21)
It is noted that the substance is used as an intermediate so that the substance is chemically transformed into another substance.
9.16.2.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Qualitative assessment
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%] The content of the substance in a sealed battery is considered as being not relevant for occupational exposure if used as intended.
Qualitative assessment
• Physical form of substance: Included in closed container Cobalt dihydroxide is in a closed container (battery)
Qualitative assessment
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Qualitative
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Method
assessment
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Qualitative assessment
Technical and organisational conditions and measures
• Process pressure: Ambient Qualitative assessment
• Process temperature: Ambient Qualitative assessment
9.16.2.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.128. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 1E-3 µg/m³ (Qualitative assessment .) RCR < 0.01
Remarks on exposure data from external estimation tools:
Qualitative assessment .: Explanation: Since batteries are considered as closed containers which cannot lead to exposure under normal condition of use, a qualitative assessment is considered sufficient.
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.17. Exposure scenario 17: Formulation or re-packing - Formulation of mixtures for use in biogas production Market sector: Use in fermentation processes, in the biotech sector and in biogas production Product category formulated: PC 0: Other
Environment contributing scenario(s):
CS 1 Formulation of mixtures for use in biogas production ES1 STP Discharge
ERC 2
CS 2 Formulation of mixtures for use in biogas production ES2 Direct Discharge
ERC 2
CS 3 Formulation of mixtures for use in biogas production ES3 Marine Discharge
ERC 2
Worker contributing scenario(s):
CS 4 Raw material handling PROC 26
CS 5 Formulation of solutions PROC 3
CS 6 Production of solid formulations PROC 3
CS 7 Filling of solutions containing <1 % of cobalt dinitrate PROC 8b
CS 8 Packaging of solid formulations containing <1 % of cobalt dinitrate
PROC 26
CS 9 Cleaning & Maintenance PROC 28
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment.
9.17.1. Env CS 1: Formulation of mixtures for use in biogas production ES1 STP Discharge (ERC 2)
9.17.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.069 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 25 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 3 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
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Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 500
9.17.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.129. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.347 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T)
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.94E-3 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.17.1.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
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Table 9.130. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.31E-4 mg/L RCR = 0.373
Sediment (freshwater) Local PEC: 9.32 mg/kg dw Clocal: 5.06 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.173
Sewage Treatment Plant Local PEC: 0.104 mg/L RCR = 0.281
Agricultural soil Local PEC: 3.162 mg/kg dw RCR = 0.29
Man via environment - Inhalation
Concentration in air: 1.9E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.17.2. Env CS 2: Formulation of mixtures for use in biogas production ES2 Direct Discharge (ERC 2)
9.17.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.069 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 25 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 3 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
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• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 1E3
9.17.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.131. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.347 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T)
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.94E-3 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.17.2.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
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Table 9.132. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.1E-4 mg/L RCR = 0.338
Sediment (freshwater) Local PEC: 8.48 mg/kg dw Clocal: 4.22 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.158
Agricultural soil Local PEC: 0.24 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.9E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.17.3. Env CS 3: Formulation of mixtures for use in biogas production ES3 Marine Discharge (ERC 2)
9.17.3.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.069 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 25 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 3 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use
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and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Marine water only
• Dilution factor to marine water: <= 800
9.17.3.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.133. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.347 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T)
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.94E-3 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.17.3.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.134. Exposure concentrations and risks for the environment and man via the environment
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Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.109 µg/L Clocal: 0.094 µg/L (estimated by Clocal calculation with Kp susp. matter marine (logKp = 4.94))
RCR = 0.046
Sediment (marine water) Local PEC: 22.8 mg/kg dw Clocal: 8.1 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.327
Agricultural soil Local PEC: 0.24 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.9E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.17.4. Worker CS 4: Raw material handling (PROC 26)
Task(s) covered with this contributing scenario: Opening of containers / dosing, immediate removal of wet splashes.
9.17.4.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
• Additional physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Monitoring data
• Shifts per year: <= 24 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) Monitoring data
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Method
[Effectiveness Inhalation: 90%] High efficiency
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.17.4.2. Exposure and risks for workers
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The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.135. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 1.6 µg/m³ (Measured data: Monitoring data) RCR = 0.013
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.17.5. Worker CS 5: Formulation of solutions (PROC 3)
Task(s) covered with this contributing scenario: Dissolution.
9.17.5.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Analogous data
• Physical form of substance: Aqueous solution Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Analogous data
• Shifts per year: <= 24 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
• Level of containment: Closed process Closed pipe system, closed reaction vessels
Analogous data
• Level of automation: Semi-automated process Analogous data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency Vapour extraction units in the tank
Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the
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Method
conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.17.5.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.136. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 6 µg/m³ (Measured data: Analogous data) RCR = 0.048
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance
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Inhalation exposure, long term concentration: Number of measured data points: 133 ; GSD: 2.56
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.17.6. Worker CS 6: Production of solid formulations (PROC 3)
Task(s) covered with this contributing scenario: Mixing, milling, sieving, blending.
9.17.6.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Analogous data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Analogous data
• Physical form of substance: Solid Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Analogous data
• Shifts per year: <= 24 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
• Level of containment: Closed process Closed pipe system, closed reaction vessels
Analogous data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency
Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general,
Analogous data
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Method
inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.17.6.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.137. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 1.6 µg/m³ (Measured data: Analogous data) RCR = 0.013
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.17.7. Worker CS 7: Filling of solutions containing <1 % of cobalt dinitrate (PROC 8b)
Task(s) covered with this contributing scenario: Filling of formulated solutions, immediate removal of wet splashes.
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9.17.7.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Content in preparation: < 1 % [Effectiveness Inhalation: 90%, Dermal: 90%] Analogous data
• Physical form of substance: Aqueous solution Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Analogous data
• Shifts per year: <= 24 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the
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Method
emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.17.7.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.138. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 5 µg/m³ (Measured data: Analogous data) RCR = 0.04
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.17.8. Worker CS 8: Packaging of solid formulations containing <1 % of cobalt dinitrate (PROC 26)
Task(s) covered with this contributing scenario: Packaging of powders, granules or other solid formulations.
9.17.8.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Analogous data
• Content in preparation: < 1 % [Effectiveness Inhalation: 90%, Dermal: 90%] Analogous data
• Physical form of substance: Solid, powder / dust Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Analogous data
• Shifts per year: <= 24 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
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Method
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
• Integrated local exhaust ventilation: Upper confidence limit (industrial use) [Effectiveness Inhalation: 90%] High efficiency
Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.17.8.2. Exposure and risks for workers
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The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.139. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 1.6 µg/m³ (Measured data: Analogous data) RCR = 0.013
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.17.9. Worker CS 9: Cleaning & Maintenance (PROC 28)
Task(s) covered with this contributing scenario: Manual cleaning, repair and maintenance operations, removal of residuals from e.g. filters/overspill or as waste.
9.17.9.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: High Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Physical form of substance: Solid, powder / dust Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 480 min Analogous data
• Shifts per year: <= 24 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
• Process pressure: Ambient Analogous data
• Additional operational conditions for cleaning and maintenance: Maintenance and repair work only at machinery/systems which are not in operation. Minor cleaning tasks may be conducted under operation.
Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Analogous data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required
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Method
Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Analogous data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.17.9.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.140. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 33.9 µg/m³ (Measured data: Analogous data) RCR = 0.273
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance
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Inhalation exposure, long term concentration: Number of measured data points: 187 ; GSD: 4.44
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.18. Exposure scenario 18: Use at industrial sites - Use in biogas production Market sector: Use in fermentation processes, in the biotech sector and in biogas production Product category used: PC 0: Other Sector of use: SU 9: Manufacture of fine chemicals
Environment contributing scenario(s):
CS 1 Use in biogas production ES1 STP Discharge ERC 4
CS 2 Use in biogas production ES2 Direct Discharge ERC 4
CS 3 Use in biogas production ES3 Marine Discharge ERC 4
Worker contributing scenario(s):
CS 4 Dosing of solid material PROC 26
CS 5 Dosing of liquid material PROC 8b, PROC 9
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment.
9.18.1. Env CS 1: Use in biogas production ES1 STP Discharge (ERC 4)
9.18.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.069 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 25 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 3 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered.
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Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 500
9.18.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.141. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.347 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T) Although ERC4 is selected for this use it is assumed that most releases will occur during the formulation step of Co compounds in a solution.
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.94E-3 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.18.1.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.142. Exposure concentrations and risks for the environment and man via the environment
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Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.31E-4 mg/L RCR = 0.373
Sediment (freshwater) Local PEC: 9.32 mg/kg dw Clocal: 5.06 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.173
Sewage Treatment Plant Local PEC: 0.104 mg/L RCR = 0.281
Agricultural soil Local PEC: 3.162 mg/kg dw RCR = 0.29
Man via environment - Inhalation
Concentration in air: 1.9E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.18.2. Env CS 2: Use in biogas production ES2 Direct Discharge (ERC 4)
9.18.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.069 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 25 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 3 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds
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waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 1E3
9.18.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.143. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.347 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T) Although ERC4 is selected for this use it is assumed that most releases will occur during the formulation step of Co compounds in a solution.
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.94E-3 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.18.2.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
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Table 9.144. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.1E-4 mg/L RCR = 0.338
Sediment (freshwater) Local PEC: 8.48 mg/kg dw Clocal: 4.22 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.158
Agricultural soil Local PEC: 0.24 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.9E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.18.3. Env CS 3: Use in biogas production ES3 Marine Discharge (ERC 4)
9.18.3.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.069 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 25 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 3 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use
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and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Marine water only
• Dilution factor to marine water: <= 800
9.18.3.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.145. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.347 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T) Although ERC4 is selected for this use it is assumed that most releases will occur during the formulation step of Co compounds in a solution.
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.94E-3 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.18.3.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following
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table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.146. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.109 µg/L Clocal: 0.094 µg/L (estimated by Clocal calculation with Kp susp. matter marine (logKp = 4.94))
RCR = 0.046
Sediment (marine water) Local PEC: 22.8 mg/kg dw Clocal: 8.1 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.327
Agricultural soil Local PEC: 0.24 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.9E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.18.4. Worker CS 4: Dosing of solid material (PROC 26)
Task(s) covered with this contributing scenario: Dosing of solid mixture into reactor.
9.18.4.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Monitoring data
• Content in preparation: < 1 % [Effectiveness Inhalation: 90%, Dermal: 90%] Monitoring data
• Physical form of substance: Solid Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 15 min Monitoring data
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
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Method
• Indoor or outdoor use: Outdoors Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.18.4.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.147. Exposure concentrations and risks for workers
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Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.049 µg/m³ (Measured data: Monitoring data)
RCR < 0.01
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.18.5. Worker CS 5: Dosing of liquid material (PROC 8b, PROC 9)
Task(s) covered with this contributing scenario: Dosing of solutions into reactor, immediate removal of wet splashes.
9.18.5.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Analogous data
• Content in preparation: < 1 % [Effectiveness Inhalation: 90%, Dermal: 90%] Analogous data
• Physical form of substance: Aqueous solution Analogous data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 15 min Analogous data
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Analogous data
Technical and organisational conditions and measures
• Process temperature: Ambient Analogous data
• Indoor or outdoor use: Outdoors Analogous data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the
Analogous data
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Method
substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.18.5.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.148. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.049 µg/m³ (Measured data: Analogous data)
RCR < 0.01
Remarks on measured exposure:
Analogous data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.19. Exposure scenario 19: Widespread use by professional workers - Professional use of formulations in biogas production Market sector: Use in fermentation processes, in the biotech sector and in biogas production Product category used: PC 0: Other
Environment contributing scenario(s):
CS 1 Professional use of formulations in biogas production ERC 8e, ERC 8b
Worker contributing scenario(s):
CS 2 Handling of sealed bags PROC 8b
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment.
9.19.1. Env CS 1: Professional use of formulations in biogas production (ERC 8e)
9.19.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily local widespread use amount: <= 2.75E-5 tonnes/day The tonnage and further exposure is always expressed in cobalt.
Conditions and measures related to biological sewage treatment plant
• Biological STP: Standard [Effectiveness Water: 40%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low risk) Fraction of daily/annual use expected in waste: 60% of all articles, 40% is recycled. (EC, 2010) Appropriate waste codes: 20 01 34, 20 01 40, 20 03 01, 20 03 07, … Suitable Disposal: Waste from end-of-life articles can be disposed of as municipal waste, except when they are separately regulated, like electronic devices, batteries, vehicles, etc. Disposal of wastes is possible via incineration (operated according to Directive 2000/76/EC on the incineration of waste) or landfilling (operated according to Reference Document on the Best available Techniques for Waste Industries of August 2006 and Council Directive 1999/31/EC and Council Decision 19 December 2002). A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.19.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.149. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor Release factor before on site RMM: 0% Release factor after on site RMM: 0% Local release rate: 0 kg/day Explanation: There are no intended cobalt releases due to the use of cobalt dinitrate formulations in the biogas production, the non-intended releases are negligible and pose no threat
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Release Release estimation method
Explanations
to the environment.
Air Estimated release factor Release factor before on site RMM: 0% Release factor after on site RMM: 0% Explanation: Not relevant
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: Not relevant
Releases to waste
Release factor to external waste: 60 % Fraction of daily/annual use expected in waste: 60% of all articles, 40% is recycled. (EC, 2010). Note that the 60% does not specifically apply to this use but applies to all professional, consumer or service life uses from cobalt. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.19.1.3. Exposure and risks for the environment and man via the environment
No exposure datasets are defined for this environmental contributing scenario.
Risk characterisation
The exposure concentrations and risk characterisation ratios (RCR) for the service life are negligible and pose no threat to the environment. Emission data from municipal STPs have been collected for Belgium (via VMM) and The Netherlands (WATSON database). For Belgium 6 data points are available between 2011 and 2013. Only one data point is above the DL, the effluent concentration of the STP above the DL is 3 µg Co/L. For the Netherlands 272 data points are available between 2005 and 2012. Only 69 data points are above the DL, the median effluent concentration is below the DL and the 90th percentile is 2.69 µg Co/L. These concentrations are a factor 100 below the PNEC for STP of 370 µg Co/L.
9.19.2. Worker CS 2: Handling of sealed bags (PROC 8b)
Task(s) covered with this contributing scenario: Loading of reactors, placing sealed biodegradable bags directly into the substrate dosing unit.
9.19.2.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment. Massive object is taken as a surrogate
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Massive object Sealed biodegradable bags
Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 15 min Monitoring data
• Shifts per year: <= 240 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
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Method
• Process temperature: Ambient Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.19.2.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.150. Exposure concentrations and risks for workers
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Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.049 µg/m³ (Measured data: Monitoring data)
RCR < 0.01
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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9.20. Exposure scenario 20: Use at industrial sites - Use in fermentation processes, in biotech and scientific research and standard analysis Market sector: Use in fermentation processes, in the biotech sector and in biogas production Product category used: PC 21: Laboratory Chemicals; PC 29: Pharmaceuticals Sector of use: SU 9: Manufacture of fine chemicals; SU 24: Scientific research and development
Environment contributing scenario(s):
CS 1 Use in fermentation processes, in biotech and scientific research and standard analysis ES1 STP Discharge
ERC 4
CS 2 Use in fermentation processes, in biotech and scientific research and standard analysis ES2 Direct Discharge
ERC 4
CS 3 Use in fermentation processes, in biotech and scientific research and standard analysis ES3 Marine Discharge
ERC 4
Worker contributing scenario(s):
CS 4 Raw material handling PROC 9, PROC 26; PROC 8b
CS 5 Operations in closed systems PROC 3, PROC 1; PROC 2
CS 6 Handling at laboratory scale PROC 15
CS 7 Handling of liquid stock solution PROC 5, PROC 3; PROC 8b; PROC 9
Explanation on the approach taken for the ES:
Please refer to IUCLID Section 13 for a detailed description of the specific methodology applied for the occupational exposure assessment.
9.20.1. Env CS 1: Use in fermentation processes, in biotech and scientific research and standard analysis ES1 STP Discharge (ERC 4)
9.20.1.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.069 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 25 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 3 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
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• Biological STP: Standard [Effectiveness Water: 40%]
• Discharge rate of STP: >= 2E3 m3/day
• Application of the STP sludge on agricultural soil: Yes
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 500
9.20.1.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.151. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.347 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T) Although ERC4 is selected for this use it is assumed that most releases will occur during the formulation step of Co compounds in a solution.
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.94E-3 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
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Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.20.1.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.152. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.31E-4 mg/L RCR = 0.373
Sediment (freshwater) Local PEC: 9.32 mg/kg dw Clocal: 5.06 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.173
Sewage Treatment Plant Local PEC: 0.104 mg/L RCR = 0.281
Agricultural soil Local PEC: 3.162 mg/kg dw RCR = 0.29
Man via environment - Inhalation
Concentration in air: 1.9E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.20.2. Env CS 2: Use in fermentation processes, in biotech and scientific research and standard analysis ES2 Direct Discharge (ERC 4)
9.20.2.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.069 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 25 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 3 companies.
Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
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• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Freshwater only
• Dilution factor to freshwater: <= 1E3
9.20.2.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.153. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.347 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T) Although ERC4 is selected for this use it is assumed that most releases will occur during the formulation step of Co compounds in a solution.
Air Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01% Local release rate: 6.94E-3 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation:
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Release Release estimation method
Explanations
No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.20.2.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.154. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Fresh water Local PEC: 2.1E-4 mg/L RCR = 0.338
Sediment (freshwater) Local PEC: 8.48 mg/kg dw Clocal: 4.22 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.158
Agricultural soil Local PEC: 0.24 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.9E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.20.3. Env CS 3: Use in fermentation processes, in biotech and scientific research and standard analysis ES3 Marine Discharge (ERC 4)
9.20.3.1. Conditions of use
Amount used, frequency and duration of use (or from service life)
• Daily use amount at site: <= 0.069 tonnes/day The tonnage and further exposure is always expressed in cobalt.
• Annual use amount at site: <= 25 tonnes/year For the generic exposure scenario a tonnage covering 100% of the sector tonnages was selected.
• Number of release days per year: >= 360 days/year The selected number of production days per year is the median value based on data from 3 companies.
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Technical and organisational conditions and measures
• Risk management measures to limit releases to air: One or more of the following measures should be present to reduce emissions to air: Electrostatic precipitators, Wet electrostatic precipitators, Cyclones as primary collector, Fabric or bag filters, Ceramic/Metal mesh filters or Wet scrubbers.
• Risk management measures to limit releases to water: One or more of the following measures should be present to reduce emissions to water: Chemical precipitation, Sedimentation, Filtration, Electrolysis, Reverse osmosis or Ion exchange.
Conditions and measures related to biological sewage treatment plant
• Biological STP: None [Effectiveness Water: 0%]
Conditions and measures related to external treatment of waste (including article waste)
• Particular considerations on the waste treatment operations: No (low amount) Wastes from onsite risk management measures and solid or liquid wastes from production, use and cleaning processes should be disposed of separately or/and with other cobalt compounds waste to hazardous waste incineration plants or hazardous waste landfills as hazardous waste. Releases to the floor, water and soil are to be prevented. If the cobalt content of the waste is elevated enough, internal or external recovery/recycling might be considered. Appropriate waste codes: 01 03 07*, 02 01 10*, 06 05 02*, 06 03 13*, 06 03 15*, 06 04 05*, 10 08 04, 10 10 03, 10 10 05*, 10 10 07*, 10 10 10, 10 10 11*, 11 02 07*, 12 01 03*, 12 01 04, 15 01 04*, 15 01 10*, 16 01 04*, 16 01 06*, 16 01 18*, 16 03 03*, 16 06 02*, 16 06 05, 16 08 02*, 16 08 03, 16 10 01*, 17 04 07*, 17 04 09*, 17 09 04*, 19 10 02*, 19 12 03*,… Suitable disposal: Keep separate and dispose of to either - Hazardous waste incineration operated according to Council Directive 2008/98/EC on waste, Directive 2000/76/EC on the incineration of waste and the Reference Document on the Best Available Techniques for Waste Incineration of August 2006. - Hazardous landfill operated under Directive 1999/31/EC. A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
Other conditions affecting environmental exposure
• Discharge rate of effluent: >= 2E3 m3/day
• Discharge to: Marine water only
• Dilution factor to marine water: <= 800
9.20.3.2. Releases
The local releases to the environment are reported in the following table. Note that the releases reported do not account for the removal in the modelled biological STP.
Table 9.155. Local releases to the environment
Release Release estimation method
Explanations
Water Estimated release factor (SpERC for formulation of metal compounds)
Release factor before on site RMM: 0.5% Release factor after on site RMM: 0.5% Local release rate: 0.347 kg/day Explanation: Eurométaux, 2012, version 2.1 The reported release factor for water is based on emissions before treatment. Reported risk management measures for wastewater is on-site WWTP (removal efficiency >75%). The release factor to water after treatment for this specific use is thus 0.5% (i.e. 5000 g/T) Although ERC4 is selected for this use it is assumed that most releases will occur during the formulation step of Co compounds in a solution.
Air Estimated release factor (SpERC for formulation
Release factor before on site RMM: 0.01% Release factor after on site RMM: 0.01%
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Release Release estimation method
Explanations
of metal compounds) Local release rate: 6.94E-3 kg/day Explanation: Eurométaux, 2012, version 2.1
Non agricultural soil
Estimated release factor Release factor after on site RMM: 0% Explanation: No direct release to soil.
Releases to waste
Release factor to external waste: 0.1 % A detailed assessment has been performed and is reported in the Waste report (ARCHE, 2011)
9.20.3.3. Exposure and risks for the environment and man via the environment
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 9.156. Exposure concentrations and risks for the environment and man via the environment
Protection target Exposure concentration Risk quantification
Marine water Local PEC: 0.109 µg/L Clocal: 0.094 µg/L (estimated by Clocal calculation with Kp susp. matter marine (logKp = 4.94))
RCR = 0.046
Sediment (marine water) Local PEC: 22.8 mg/kg dw Clocal: 8.1 mg/kg dw (estimated by PEC sediment calculation method for metals local PEC = Clocal,sed + PECreg,sed))
RCR = 0.327
Agricultural soil Local PEC: 0.24 mg/kg dw RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.9E-6 mg/m³ RCR < 0.01
Man via Environment - Oral Exposure via food consumption: 0.317 µg/kg/d
RCR = 0.011
Man via environment - combined routes
Not required (local and systemic effects)
Risk characterisation
MAN VIA ENVIRONMENT: The use of EUSES to predict the concentration in food is difficult to apply for metals and associated with much higher uncertainties than using measured data. Therefore, deviations from the TGD food basket approach for the exposure route “ingestion of food”, have been applied as shortly described in the introductory section 9.0.. The oral exposure concentration in µg/kg bw/day has been derived by taking 2L of drinking water (PEC freshwater taken from the local environmental exposure assessment) + the worst case exposure from food (see introductory section 9.0.) and a default body weight of 60kg into account. Furthermore, the exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
9.20.4. Worker CS 4: Raw material handling (PROC 9, PROC 26; PROC 8b)
Task(s) covered with this contributing scenario: Opening of containers / dosing, immediate removal of wet splashes.
9.20.4.1. Conditions of use
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Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 48 min Monitoring data
• Shifts per year: <= 31 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
• Generic local exhaust ventilation: Lower confidence limit (industrial use) [Effectiveness Inhalation: 78%] Standard efficiency
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• Chemical protective suit according to EN 13982 In cases where direct contact with the substance cannot be avoided, a protective suit conforming to EN 13982 should be worn.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice
Monitoring data
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Method
and proper use of personal protective equipment (if relevant) is required.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.20.4.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.157. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.2 µg/m³ (Measured data: Monitoring data) RCR < 0.01
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.20.5. Worker CS 5: Operations in closed systems (PROC 3, PROC 1; PROC 2)
Task(s) covered with this contributing scenario: Operations in closed systems.
9.20.5.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
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Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 251 min Monitoring data
• Shifts per year: <= 78 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Level of containment: Closed process Except for handling at laboratory scale.
Monitoring data
• Process temperature: Ambient Monitoring data
• Generic local exhaust ventilation: Lower confidence limit (industrial use) [Effectiveness Inhalation: 78%] Standard efficiency
Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless
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Method
contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.20.5.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.158. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.8 µg/m³ (Measured data: Monitoring data) RCR < 0.01
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.20.6. Worker CS 6: Handling at laboratory scale (PROC 15)
Task(s) covered with this contributing scenario: Handling at laboratory scale.
9.20.6.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Medium Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.)
Monitoring data
• Content in preparation: Not restricted [Effectiveness Inhalation: 0%, Dermal: 0%]
Monitoring data
• Physical form of substance: Solid, powder / dust Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 113 min Monitoring data
• Shifts per year: <= 34 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
• Generic local exhaust ventilation: Lower confidence limit (industrial use) Monitoring data
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[Effectiveness Inhalation: 78%] Standard efficiency
Conditions and measures related to personal protection, hygiene and health evaluation
• Respiratory protective equipment (RPE): RPE with minimum APF = 10 [Effectiveness Inhalation: 90%] APF = assigned protection factor according to EN 529. At minimum any combination of particle filter class P2 with mask according to EN 140, EN 1827 or EN 136 or filtering half mask (FF P2) according to EN 149 or combination of P1 filter with face piece according EN 12942 or any RPE providing higher APFs according to EN 529 is required.
Monitoring data
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
Monitoring data
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
9.20.6.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
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Table 9.159. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.4 µg/m³ (Measured data: Monitoring data) RCR < 0.01
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
9.20.7. Worker CS 7: Handling of liquid stock solution (PROC 5, PROC 3; PROC 8b; PROC 9)
Task(s) covered with this contributing scenario: Dissolution in water, mixing, further handling of stock solution, sampling, immediate removal of wet splashes.
9.20.7.1. Conditions of use
Method
Product (article) characteristics
• Maximum emission potential of the substance: Very low Only the highest emission potential (EP) is reported. Lower EPs (e.g. if materials of lower dustiness are being handled in parallel) are thus automatically covered in this assessment.
Monitoring data
• Content in preparation: 1 - 5 % [Effectiveness Inhalation: 80%, Dermal: 80%] Monitoring data
• Physical form of substance: Aqueous solution Monitoring data
Amount used (or contained in articles), frequency and duration of use/exposure
• Duration per shift: <= 199 min Monitoring data
• Shifts per year: <= 81 Shifts/year Typical number of shifts per year during which this task is conducted considering a single worker. This value has been taken into account in the calculation of excess cancer risk.
Monitoring data
Technical and organisational conditions and measures
• Process temperature: Ambient Monitoring data
Conditions and measures related to personal protection, hygiene and health evaluation
• Gloves: Gloves protecting from sensitizing properties to skin, continuous supervision of workers required Due to the skin sensitizing effect of the substance, protective gloves according to EN 374 have to be worn at all workplaces unless any exposure to the substance can be excluded when taking into account the nature of the conducted process, applied exposure prevention measures and physical appearance of the substance of concern in the specific type of application (e.g. protecting from splashes by containment of emission source). Gloves have to be changed according to manufacturer’s information or when damaged, whatever is the earlier. Additionally, face protection is required to be worn as appropriate. This level of protection is to be achieved by continuous supervision and training of workers wearing gloves.
• General good occupational hygiene practices Required good occupational hygiene practices to ensure a safe handling of the
Monitoring data
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Method
substance involve measures (e.g. shower and change clothes at end of work shift) to avoid any contamination of private households via the work-home-interface and housekeeping practices (i.e. regular cleaning with suitable cleaning devices), no eating and smoking in the workplace. In general, inhalation and ingestion should be avoided. Unless otherwise stated below, certified working clothing and shoes should be worn during work. Any contaminated clothing should not be taken home. Good general ventilation in the workplace should be ensured. Dust should not be blown off (e.g. from dried splashes) with compressed air. Regular training in workplace hygiene practice and proper use of personal protective equipment (if relevant) is required.
• Certified safety clothing and shoes Certified safety clothing including coveralls and safety shoes are to be worn as appropriate. Face protection may be worn if the type of process is associated with the risk of face injuries due to thermal or mechanical stress.
• Eye protection: Eye protection to be worn to protect from eye damage Eye protection: Eye protection to be worn to protect from eye damage (Due to the eye damaging properties of the substance, direct contact with the eyes is to be avoided including hand to eye transfer after touching contaminated surfaces. Suitable eye protection equipment (e.g. goggles or visors) must be worn, unless contact of the substance with the eyes can be excluded. Such exclusion is determined by: (i) the physical appearance of the substance in the specific type of application (e.g. wetting the substance can effectively prevent from the emission of dust), (ii) the emission potential resulting from the nature of the process (e.g. splashes, emission of dust can be excluded in a closed process) and (iii) applied exposure prevention measures (segregation of the emission source or separation of the worker from the emission source). Additionally, face protection may be required to be worn in such cases as appropriate.)
• Respiratory protective equipment (RPE) as precautionary measure: RPE protecting from local effects via inhalation Due to potential adverse effects of the substance to the respiratory tract, RPE (minimum assigned protection factor of 10) is prescribed on a precautionary basis for all workplaces unless inhalation exposure to the substance can be excluded.
9.20.7.2. Exposure and risks for workers
The exposure concentrations and risk characterisation ratios (RCR) are reported in the following table.
Table 9.160. Exposure concentrations and risks for workers
Route of exposure and type of effects
Exposure concentration Risk quantification
Inhalation, local, long term 0.6 µg/m³ (Measured data: Monitoring data) RCR < 0.01
Remarks on measured exposure:
Monitoring data: Identity of the substance used: Exposure reported as substance Inhalation exposure, long term concentration: Number of measured data points: 6 ; GSD: 1
Risk characterisation
Qualitative risk characterisation (Inhalation, local, acute, Dermal, local, long term , Dermal, local, acute, Eye, local): Further information on the risk characterisation for local effects via inhalation and for local effects on the skin and to the eyes is given in Section 9.0.4.2.
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10. RISK CHARACTERISATION RELATED TO COMBINED EXPOSURE
10.1. Human health
10.1.1. Workers
Combined exposure relevant for workers may occur in any of the following scenarios:
1. Multiple cobalt substances handled in parallel at the same workplace,
2. Combination of the inhalation and dermal exposure route,
3. More than just a single contributing occupational scenario relevant for a specific worker, and
4. Workers that are also exposed to cobalt in their free time (e.g. as member of the general
population or as consumer).
These scenarios are considered below: Multiple cobalt substances handled in parallel at the same workplace: Inhalation exposure monitoring data were obtained from a number of workplaces where cobalt and/or cobalt substances are manufactured or handled in parallel. Sampled dust is subsequently analysed for its cobalt content but further chemical speciation is normally not done. Thus, measured cobalt levels as reported above, are in most cases already reflective of parallel exposure to a variety of cobalt substances and not only relevant for a single cobalt substance. Exposure estimates are reported in µg Co/m³ and are back-calculated to other cobalt substances by taking into account the molecular weight of the specific substance for which exposure needs to be assessed and without further modification. Thus, in the assessment for this specific cobalt substance contribution to cobalt exposure from other cobalt substances handled in parallel is intrinsically included. The approach therefore intrinsically represents a combined exposure assessment for workers so that further summation of RCRs for different cobalt substances is not appropriate. Combination of the inhalation and dermal exposure route: Since systemic effects are not relevant for the assessed cobalt substances, a summation of RCRs for the dermal and inhalation route is not required. More than just a single contributing occupational scenario relevant for a specific worker: Safe use has been demonstrated for individual contributing scenarios (CES) above by taking into account the exposure duration relevant for this CES. If the associated exposure duration considered was significantly less than full-shift (i.e. 480 minutes, it is possible that a single worker continues his shift in another CES involving handling/processing of the substance. As a worst case approach, one could consider summing up all CES-specific RCRs that are relevant for a single ES. Since the exposure duration for all CESs together does often significantly exceed 480 minutes, the aforementioned approach would often lead to an unrealistic estimation of the risk of combined exposure. An alternative approach is proposed below, that addresses the combined risk assessment from a semi-quantitative perspective: When reviewing the average and maximum RCR values for the individual CSRs of the 5 cobalt salts, it can easily be seen that RCRs were generally kept at a low level (See table below).
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Table 10.1. Summary of maximum RCRs and sums of RCRs per ES
ES CoCO3 Co(C2H3O2)2 CoCl2 Co(NO3)2 CoSO4
Max Sum Max Sum Max Sum Max Sum Max Sum
01 0.183 0.741 0.161 0.456 0.183 0.741 0.183 0.739 0.183 0.739
02 0.031 0.031 0.139 0.152 0.030 0.043 0.031 0.044 0.117 0.139
03 0.134 0.146 0.078 0.078 0.117 0.129 0.215 0.400 0.048 0.048
04 0.084 0.216 0.021 0.040 0.021 0.040 0.117 0.128 0.021 0.049
05 0.021 0.049 0.210 0.240 0.210 0.240 0.035 0.089 0.210 0.246
06 0.210 0.246 0.035 0.039 0.035 0.039 0.021 0.040 0.035 0.039
07 0.035 0.039 0.210 0.448 0.210 0.506 0.210 0.240 0.210 0.475
08 0.210 0.523 0.023 0.023 0.032 0.032 0.035 0.039 0.027 0.027
09 0.035 0.035 0.023 0.023 0.032 0.032 0.210 0.451 0.027 0.027
10 0.035 0.035 n.r. n.r. 0.374 0.647 0.023 0.023 0.374 0.647
11 0.374 0.647 0.453 n.a. 0.003 0.003 0.023 0.023 0.003 0.003
12 0.003 0.003 0.445 0.681 0.453 n.a. 0.374 0.647 0.022 0.056
13 0.453 n.a. 0.007 0.007 0.068 0.121 0.003 0.003 <0.001 <0.001 14 0.052 0.126 0.007 0.007 0.047 0.119 0.043 0.107 <0.001 <0.001 15 0.273 0.398 n.r. n.r. 0.273 0.391 <0.001 <0.001 0.453 n.a.
16 <0.001 0.001 0.035 0.101 <0.001 0.001 <0.001 <0.001 0.057 0.064
17 <0.001 <0.001 0.050 0.057 <0.001 <0.001 0.273 0.399 0.040 0.107
18 0.007 0.016 0.520 0.595 0.007 0.016 <0.001 0.001 0.273 0.380
19 <0.001 <0.001 0.012 0.014 <0.001 <0.001 <0.001 0.001
20 <0.001 <0.001 <0.001 <0.001 0.007 0.016 <0.001 <0.001
21 0.007 0.016 0.007 0.016
n.a.: Since the risk characterisation is based on full-shift exposure duration for these CES, a combined CES assessment is not required; instead the maximum RCR is to be considered. n.r.: ES represents a consumer ES and is therefore not considered in this table. As can be seen above all RCR sums (respectively maximum RCRs) are well below 1 indicating that combined exposure is well controlled in each ES of the 5 cobalt salts. Workers that are also exposed to cobalt in their free time (e.g. as member of the general population or as consumer): For workers who are members of other populations to be protected in this chemical safety assessment (i.e. consumers and/or general population), a specific combined exposure assessment is not required as workers represent a less vulnerable population in comparison to subpopulations (e.g. children) which may be considered in assessments for the general population. Any RCR from these subpopulations could safely be assumed to be in fact significantly lower if re-calculated for workers. In a combined assessment of exposure, one would also avoid adding the worst case RCR for workers with the worst case RCR of another population as this would lead to an unrealistic scenario. Instead typical RCRs would be taken which would in combination lead to a low combined RCR.
10.1.2. Consumer
A combined exposure assessment is not applicable as there are no consumer-related uses/service life scenarios for the substance.
10.2. Environment (combined for all emission sources)
10.2.1. All uses (regional scale)
10.2.1.1. Total releases
The total releases to the environment from all the exposure scenarios covered are presented in the table below. This is the sum of the releases to the environments from all exposure scenarios addressed. Where there is more than one contributing scenario for the environment for a given exposure scenario, the highest release per route across all the contributing scenarios within the use has been
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taken into account as the release for the use (both for the regional and the exposure due to all the widespread uses). This may lead to overestimation of the PEC.
Table 10.2. Total releases to the environment per year from all life cycle stages
Release route Total releases per year
Water 4.11E3 kg/year
Air 1.84E3 kg/year
Soil 0 kg/year
10.2.2. Regional assessment
The regional predicted environmental concentration (PEC regional) and the related risk characterisation ratios when a PNEC is available are presented in the table below. The exposure to man via the environment from regional exposure and the related risk characterisation ratios are also provided (when relevant). The exposure concentration for human via inhalation is equal to the PEC air. The exposure estimates have been obtained with EUSES 2.1.2 unless stated otherwise.
Table 10.3. Predicted regional exposure concentrations (Regional PEC) and risks for the environment
Protection target Regional PEC Risk characterisation
Fresh water Regional PEC: 0.1 µg/L (See below) RCR = 0.161
Sediment (freshwater) Regional PEC: 4.26 mg/kg dw (See below)
RCR = 0.079
Marine water Regional PEC: 0.015 µg/L (See below)
RCR < 0.01
Sediment (marine water) Regional PEC: 14.7 mg/kg dw (See below)
RCR = 0.211
Agricultural soil Regional PEC: 0.239 mg/kg dw (See below)
RCR = 0.022
Man via environment - Inhalation
Concentration in air: 1.56E-7 ng/m³ (See below)
RCR < 0.01
Man via environment - Oral Exposure via food consumption: 0.2 µg/kg bw/day (Measured data: Measured data)
RCR < 0.01
Man via environment - combined routes
Not required (local and systemic effects)
EUSES 2.0 is used for calculating the regional PECadd values for each environmental compartment. The Co inputs for the regional assessment are the anthropogenic point and diffuse emissions to air, wastewater, surface water, agricultural soil and industrial/urban soil. More information available in the CSR in section “Diffuse source analysis and modeled PEC (EUSES)”. Man via environment - Inhalation Calculated regional air background concentration (EUSES model) Man via environment - Oral 2L of drinking water (0.023 µg Co/L: median value from the “Geochemistry of European Bottled Water”) + the typical exposure from food (12 µg/d: median value from the 1994 UK total diet study) and the default body weight of 60kg have been taken into account. Remarks on risk characterisation for regional concentrations: Conclusion: The risk characterisation ratios (PECadd/PNECadd) for the different compartments are all below 1. Hence no regional risks for the different environmental compartments are predicted on the basis of modelled (EUSES) data.
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MAN VIA ENVIRONMENT The exposure assessment is based on the cobalt ion, as this is the toxic species, as such for the risk characterisation the DNELs based on cobalt were used.
Diffuse source analysis and modelled PEC (EUSES)
An extended analysis of the diffuse sources for cobalt has recently been initiated (CDI, 2010). Emission of cobalt to the different compartments (air, soil, surface water) for the selected region is presented in Table 10.4 a regional emission of 1477.2 kg Co/year to the air compartment, 778.5 kg Co/year to the surface water and 16474.2 to the soil compartment were noted.
Table 10.4. Regional emission of cobalt (kg Co/year) to the different environmental compartments
Emission source Air (kg Co/year)
Surface water
(kg Co/year)
Soil (kg
Co/year) Total
Industry 528.66 485.00 / 1013.66
Traffic
- Combustion of LPG by road
traffic 709.50 / / 709,50
Agriculture
- Use of fertilisers manure and
sewage sludge on agricultural
land / / 16468.00 16468.00
- Soil erosion / / / 0
Households
- Fossil fuel burning 0
* Coal 91.20 / / 91.20
* LPG 28.80 / / 28.80
- Use of compost / / / 0
- Tobacco smoke / / / 0
Waste management
- Incineration / 44.00 / /
- Incineration 119.00 43.00 / /
- STP / 194.00 / /
- Domestic wastewater
discharge / 12.51 6.21 18.72
TOTAL 1477.16 778.51 16474.21 18329.88
A continental emission of 316771.5 kg Co/year to the air compartment, 90895.9 kg Co/year to the surface water and 345273 kg Co/year to the soil compartment were noted (Table).
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Table 10.5. Continental (EU-27 + Norway) emission of cobalt (kg Co/year) to the different environmental compartments
Emission source Air (kg Co/year)
Surface water (kg
Co/year) Soil (kg Co/year) Total
Industry 3427.00 3144.00 / 6571.00
Traffic
- Combustion of LPG by road traffic 8982.30 / / 8982.30
Agriculture
- Use of fertilisers manure and
sewage sludge on agricultural land / / 330650.00 330650.00
- Soil erosion 0 2.45 0 2.45
Households
- Fossil fuel burning
* Coal 198220.80 / / 198220.80
* LPG 104955.00 / / 104955.00
- Use of compost / / 6928.00 6928.00
- Tobacco smoke 0.83 / 66.99 67.82
Waste management
- Incineration 1185.54 430.57 / 0
- Landfilling / 1233.90 / 0
- STP / 70598.00 / 0
- Domestic wastewater discharge / 15487.00 7628.00 23115.00
TOTAL 316771.47 90895.92 345272.99 679492.37
EUSES 2.0 is used for calculating the regional PEC values for each environmental compartment. The Co inputs for the regional assessment are the anthropogenic point and diffuse emissions to air, wastewater, surface water, agricultural soil and industrial/urban soil (as presented in Table). The input of chemicals is regarded in the model as continuous and equivalent to continuous diffuse emission. For metals, all individual compounds are assumed to transform into the ionic species. The results from the models are steady-state concentrations, which can be regarded as estimates of long-term average exposure levels. In the continental model, it is assumed that all anthropogenic Co emissions enter into the continental environment. It is also assumed that no inflow of air and water across the boundaries of the continent occurs. Continental exposure concentrations are calculated based on the combined anthropogenic Co emissions from all EU countries (extrapolated) and on the natural/pristine ambient background of Co. An overview of the added regional exposure concentrations for the different compartments is summarised in Table 10.6.
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Table 10.6. Calculated PECadd regional for the different environmental compartments
Compartment Regional PECadd
surface water (total) 0.151 µg/L
sea water (total) 0.0174 µg/L
surface water (dissolved) 0.10 µg/L
sea water (dissolved) 0.015 µg/L
air 1.56E-13 mg/m3
agricultural soil (total) 0.239 mg/kg dw
porewater agricultural soil 1.99E-03 mg/L
natural soil 1.23E-02 mg/kg dw
industrial soil 0.0128 mg/kg dw
sediment 4.26 mg/kg dw
marine sediment 0.65 mg/kg ww
Measured background concentrations
Freshwater
The baseline background concentrations of cobalt in freshwaters generated from the FOREGS monitoring program are summarised in Table 10.7.
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Table 10.7. Baseline cobalt concentrations (in g/L) in European surface water (data from FOREGS Geochemical Baseline Program)
Country 50th percentile (g/L) 90th percentile (g/L)
Austria 0.11 0.25
Belgium 0.20 0.54
Czech republic 0.17 0.38
Denmark 0.80 1.77
Estonia 0.15 0.21
Finland 0.20 0.93
France 0.16 0.38
Germany 0.15 0.61
Greece 0.09 0.14
Hungary 0.22 0.46
Ireland 0.23 0.45
Italy 0.15 0.87
Latvia 0.16 0.21
Lithuania 0.21 0.31
Norway 0.05 0.22
Poland 0.28 0.58
Portugal 0.14 0.51
Slovakia 0.23 0.43
Slovenia Mean: 0.12 /
Spain 0.13 0.55
Sweden 0.10 0.82
The Netherlands 0.30 0.39
United Kingdom 0.18 0.76
Albania Mean: 0.07 /
Croatia 0.19 0.39
Switzerland 0.14 0.34
Median for Europe: 0.44
Median for EU-27 + Norway: 0.45
Dissolved cobalt levels ranged between 0.01 and 19.5 µg Co/L. The median value of the calculated, country-specific 50th percentiles is considered as a reliable value for a “typical” Co-baseline level in
EU surface waters. Taking all European countries into account, this value is 0.45 g/L. Discarding the
data for Albania, Croatia and Switzerland, a value of 0.44 g/L is derived for the EU (incl. Norway). Taking into account the high quality of the data set, the median value of 0.44 µg/L can be accepted as a typical background concentration for cobalt in European surface waters (Europe-regional scale).
Freshwater sediment
The baseline background concentrations of cobalt in freshwater sediments generated from the FOREGS monitoring program are summarised in Table 10.8.
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Table 10.8.Baseline cobalt concentrations (in mg/kg) in European freshwater sediments (data from FOREGS Geochemical Baseline Program)
Country 50th percentile (mg/kg dw) 90th percentile (mg/kg dw)
Austria 6.10 24.1
Belgium 12.6 27.7
Czech republic 12.7 23.4
Denmark Mean: 2.1 /
Estonia 2.27 4.42
Finland 6.88 15.4
France 7.03 16.2
Germany 6.67 14.8
Greece 14.3 26.2
Hungary 4.82 11.9
Ireland 15.0 28.3
Italy 9.16 20.8
Latvia 3.00 9.69
Lithuania 5.04 8.64
Norway 7.99 19.1
Poland 2.04 5.74
Portugal 10.6 19.8
Slovakia 9.86 14.2
Slovenia 8.66 16.7
Spain 7.88 15.4
Sweden 6.93 17.49
The Netherlands 2.38 8.30
United Kingdom 19.9 37.5
Albania Mean: 21.0 /
Croatia 8.80 13.2
Switzerland 7.04 17.1
Median for Europe 16.5
Median for EU-27 + Norway 16.7
The median value of the calculated, country-specific 50th percentiles is considered as a reliable value for a “typical” Co-baseline level in EU surface waters. Taking all European countries into account, this value is 16.5 mg/kg. Discarding the data for Albania, Croatia and Switzerland, a value of 16.7 mg/kg is derived for the EU (incl. Norway). Taking into account the high quality of the data set, the median value of 16.7 mg/kg dw can be accepted as a typical background concentration for cobalt in European freshwater sediment (Europe-regional scale).
Soil
Country-specific measured concentrations are available in natural soils for the countries reported in Table 10.9. The range of total soil Co concentrations in natural soils varies between 5.4 and 25 mg Co/kg dw.
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Table 10.9. Measured regional PEC values for natural soils in different countries
Country 50th percentile (mg/kg dw) 90th percentile (mg/kg dw)
Austria 9.71 27.1
Belgium 12.7 17.0
Czech republic 7.75 14.8
Denmark / /
Estonia 3.32 7.54
Finland 2.62 7.37
France 8.84 18.1
Germany 5.13 18.3
Greece 16.9 34.5
Hungary 6.46 17.9
Ireland 6.85 16.9
Italy 10.9 23.6
Latvia 3.95 12.9
Lithuania 2.70 7.19
Norway 4.23 10.6
Poland 1.70 5.46
Portugal 5.86 16.7
Slovakia 8.76 21.0
Slovenia 17.4 21.3
Spain 8.04 20.0
Sweden 3.14 7.16
The Netherlands 2.04 6.97
United Kingdom 6.48 20.3
Albania / /
Croatia 13.4 21.3
Switzerland 8.02 25.0
Median for the EU: 16.1
Median for the EU + Norway: 15.6
The median value of the calculated, country-specific 50th percentiles is considered as a reliable value for a “typical” Co-baseline level in EU top soils. Taking all European countries into account, this value is 16.1 mg/kg. Discarding the data for Albania, Croatia and Switzerland, a value of 15.6 mg/kg is derived for the EU (incl. Norway).
Measured ambient PEC values
The following measured PEC regional values were extracted from literature.
Freshwater
For the freshwater compartment, country-specific measured regional PECs (µg dissolved Co/L) were calculated for sites located in the countries reported in Table 10.10.
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Table 10.10. Measured regional PEC values for the freshwater in different countries.
Country Regional RWC-ambient - Co PECs (g/L)
Cototal Codissolved Not specified
Belgium–Flanders 1.78 / /
Finland / 1.01 /
The Netherlands / 0.65 /
Sweden / / 0.24
Belgium / 1.81 /
Sweden / 0.68 /
France (data for Seine) / 0.071 /
Spain / 1.08 /
United Kingdom / 1.38 /
Regional RWC-ambient PEC: 0.86 g Codiss./L
The median ambient regional PEC for Europe; i.e. 0.86 µg dissolved Co/L is used for sites located in other EU countries.
Marine water
For the marine water compartment, specific measured regional PECs (µg dissolved Co/L) were calculated for sites reported in Table 10.11.
Table 10.11. Measured regional PEC values for the marine water at different locations
Location Mean / Median concentration
(range, excl. outliers) ng/L
Ambient PEC (ng/L)
Central/Southern North Sea 8.8 (1.6 - 68.9) 35.1
Atlantic Ocean / Azores (open ocean) 2.10 (0.85 - 6.07) 4.4
Mediterranean area 20 /
Aegean Sea (Greece) 16.3 - 16.5 (median) 65.4
Surf zone water, Baja California 16.5 (median) (6.5 - 34.8) 27.8
Coastal zone water 5-45 km offshore Baja
California
2.2 (median) (1.3 - 10) 8.4
Ocean / (1.8 - 450) /
Seawater (unspecified) 270 (35 - 4100) /
Seawater (unspecified) 590 /
Open coastal pacific Ocean 40 /
North Australian waters (coastal, estuarine) 27.0 (5.4 - 67.6) 58.9
Florida, Indian River Lagoon (USA 29.3 (6 - 50) 47.2
50P: 17.8 ng/L
90P: 57.4 ng/L
open ocean: 4.4 - 8.4 ng/L
coastal: 50P of 46.7 ng/L
The range of dissolved Co concentrations in marine waters vary between 0.0044 and 0.0654 ng dissolved Co/L. For local sites discharging to a marine environment the median ambient PEC for coastal waters of 0.047 µg dissolved Co/L is used as a regional background value.
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Freshwater sediment
For the freshwater sediments, country-specific measured regional PECs (mg Co/kg dw) for sites located in the countries reported in Table 10.12.
Table 10.12. Measured regional PEC values for the freshwater sediments in different countries
Country Regional RWC-ambient Co-PECs (mg/kg dry wt)
United Kingdom 24.8
Spain 14.2
Finland 18.9-45.1
Belgium 23.6
France 16.4
Sweden 29.4
Range: 14.2 – 45.1
Regional RWC-ambient PEC: 23.8 mg/kg dw
The measured Co sediment concentrations in EU countries vary between 14.2 and 45.1 mg Co/kg dw. The median ambient regional PEC for Europe i.e. 23.8 mg Co/kg dw is used for sites located in other EU countries.
Marine Sediment
For the marine sediments, country-specific measured regional PECs (mg Co/kg dw) for sites located in the countries reported in Table 10.13.
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Table 10.13. Measured regional PEC values for the marine sediments at different locations
Location Mean / Median concentration (range,
excl. outliers) in mg/kg dw
Ambient PEC (mg/kg dw)
Baltic Sea 3.5 (0.69 - 18.1) 13.1
Gulf of Saronikos (Greece) 9.7 (5.1 - 12.7) 12.1
Gulf of Cadiz (Spain) 8.1 (3.4 - 11.5) 11.5
Red Sea 4.5 (1.6 - 10) 10.4
Black Sea 2.52 (1.3 - 4.6) /
Black Sea 14.7 -15.8 (7 - 37) 22.5
Black Sea 24 (21-27) /
Sea of Marmara 2.05 (9 - 30) /
Mersin Bay 25.5 (11 - 40) /
Coastal sediment near Stockholm
(Sweden)
15.3 /
Atlantic Ocean 19 /
Bristol Channel (United Kingdom) 11.2 (6.4 - 16) /
Massachusetts (USA): outer harbour 7.0 (3.6 - 9.8) /
Massachusetts (USA): inner harbour 6.4 (2.6 - 10.5) /
Massachusetts (USA): control site 4.8 (1.6 - 8.2) /
Ross Sea, Antarctica 1.9 ± 3.4 (0.1 - 13) /
Indian River Lagoon, Florida (USA) 1.8 (0.4 - 6.3) 5.0
Gulf of Mexico: coastal areas 27.6 35.5
Beaufort Sea 89 (± 14) /
Chukchi Sea (Alaska, USA) 3.02 (16.0 - 74.0) 47.5
50P: 6.99 mg/kg DW
90P: 24.8 mg/kg DW
Average: 19.7 (5.0 –
47.5)
Median: 14.7
The range of Co concentrations in marine sediments varies between 5.0 and 47.5 mg Co/kg dw. For sites discharging to a marine environment; the median ambient PEC for Europe of 14.7 mg Co/kg dw is used as a regional background value.
Soil
Country-specific measured concentrations are available in grazing soils for the countries reported in Table 10.14. The range of total soil Co concentrations in grazing soils varies between 5.2 and 51.6 mg Co/kg dw.
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Table 10.14. Measured regional PEC values for grazing soils in different countries
Country 50th percentile (mg/kg dw) RWC-ambient PEC (mg/kg dw)
Austria 11.4 17.0
Belgium 7.3 15.0
Bosnia 16.8 24.3
Bulgaria 11.5 16.7
Croatia 18.7 24.3
Cyprus 14.9 21.1
Czech Republic 10.0 17.7
Denmark 1.8 5.2
Estonia 3. 6.3
Finland 3.5 6.7
France 7.8 16.2
Germany 6.4 15.0
Greece 15.6 26.1
Hungary 7.9 13.2
Ireland 7.5 11.6
Italy 13.1 20.6
Latvia 3.6 7.9
Lithuania 3.7 5.8
Macedonia 13.9 17.2
Macedonia 20.2 30.8
the Netherlands 2.6 8.2
Norway 5.0 11.5
Poland 2.6 8.7
Portugal 4.3 16.0
Serbia 14.2 23.4
Slovakia 12.2 17.3
Slovenia 21.5 51.6
Spain 6.6 14.9
Sweden 3.4 10.8
Switzerland 8.2 14.4
Ukraine 5.7 11.7
United Kingdom 8.1 14.6
Median for the EU: 16.9
Median for the EU + Norway: 14.8
Country-specific measured concentrations are available in agricultural soils for the countries reported in Table 10.15. The range of total soil Co concentrations in agricultural soils varies between 5.4 and 42.7 mg Co/kg dw.
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Table 10.15. Measured regional PEC values for agricultural soils in different countries
Country 50th percentile (mg/kg dw) RWC-ambient PEC (mg/kg dw)
Austria 11.2 15.1
Belgium 8.2 24.9
Bosnia Herzegovina 18.5 26.2
Bulgaria 13.4 20.1
Croatia 13.5 26.1
Cyprus 14.4 21.4
Czech republic 9.7 17.7
Denmark 2.2 6.1
Estonia 3.6 5.4
Finland 4.4 12.7
France 7.4 19.0
Germany 5.4 21.5
Greece 16.9 32.6
Hungary 7.6 16.3
Ireland 8.9 17.0
Italy 12.1 21.1
Latvia 3.9 9.2
Lithuania 3.9 7.4
Macedonia 14.9 27.9
Montenegro 24.1 37.4
The Netherlands 2.3 10.4
Norway 5.7 14.5
Poland 2.6 8.4
Portugal 4.8 16.0
Switzerland 8.8 14.2
Slovakia 12.1 19.5
Slovenia 22.4 42.7
Spain 6.4 14.9
Serbia 15.0 22.7
Sweden 4.7 11.5
Ukraine 4.9 16.1
United Kingdom 8.1 18.1
Median for the EU: 17.3
Median for the EU + Norway: 16.3