distributions of 3,3 ’,4,4 ’,5-pexb in fecl 3 tetra-, penta-, hexa-, and hepta-xb. in fecl 3...

1
3,3',4,4',5-PeXB 0 1 PCB-126 MonoBr DiBr X X X X X Br 0Cl 5 Br 1Cl 4 Br 2Cl 3 Distributions of 3,3 ,4,4 ,5- PeXB in FeCl 3 tetra-XB penta-XB hexa-XB hepta-XB 3,3',4,4',5- 3,3',4,4',5,5'- 2,3,3',4,4',5,5'- 3,3',4,4'- X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X tetra-, penta-, hexa-, and hepta-XB. in FeCl 3 32 36 40 44 48 0 71442 Br2T3CB 32 36 40 44 48 0 1382993 BrT4CB 32 36 40 44 48 0 5678926 P5CB 32 36 40 44 48 R etention Tim e (m in) 0 1578810 13C-P 5 CB #126 M Br-#126 DiB r-#126 #126 #105 #114 #123 #118 32 36 40 44 48 0 71442 Br2T3CB 32 36 40 44 48 0 1382993 BrT4CB 32 36 40 44 48 0 5678926 P5CB 32 36 40 44 48 R etention Tim e (m in) 0 1578810 13C-P 5 CB #126 M Br-#126 DiB r-#126 #126 #105 #114 #123 #118 28 32 36 40 44 48 52 0 160936 BrH6CB 28 32 36 40 44 48 52 0 2691689 BrP5CB 28 32 36 40 44 48 52 0 2250853 BrT4CB 28 32 36 40 44 48 52 R etention Time (min) 1093 83433 BrT3CB M Br-#126 M Br-#169 M Br-#189 28 32 36 40 44 48 52 0 160936 BrH6CB 28 32 36 40 44 48 52 0 2691689 BrP5CB 28 32 36 40 44 48 52 0 2250853 BrT4CB 28 32 36 40 44 48 52 R etention Time (min) 1093 83433 BrT3CB M Br-#126 M Br-#169 M Br-#189 X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X Etching liquid Etching waste Steel plant converter dust iron powder Recycle plant FeCl3 FeCl2 Cl2 Etching plant Fe Cu water treatment Ni Coagulant printed circuit board etching plant 13 C coPCB PC B -126 C o-PC B FeC l 3 STD PeCB Co-PCB 0.0 100.0 #81 #77 #126 #169 TEQ(%) /L Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl #16 9 #169 HxCB FeCl3 STD DETECTION OF POLY HALOGENATED BIPHENYLS IN THE FeCl 3 MANUFACTURING PROCESS Nakano T , Matsumura C, Tsurukawa M, and Moriguchi Y Hyogo Prefectural Institute of Public Health and Environmental Sciences, 3-1-27 Yukihira-cho, Suma-ku, Kobe, 654-0037 Japan (A) (B) (C) F e C u C u B r P b F e F e Z n N i M n C r F e Z n N i M n F e F e Z n N i M n C u C u P b C r (A) (B) (C) F e C u C u B r P b F e F e Z n N i M n C r F e Z n N i M n F e F e Z n N i M n C u C u P b C r Etching FeCl2 FeCl3 raw water w arm ing bath contactoxidation nitrification denitrification re-aeration rapidly -stirring slow ly-stirring coagulation ba th neutralization sterilization bath 0 40 80 120 160 effluentbath H3PO4 NaO H H2SO4 N aO H N aO H M eO H FeC l 3 N aO H H2SO4 N aO H H2SO4 sodium hypochlorite N aClO [Al 2(O H) nCl 6-n] m 12.5m 3 224m 3 24m3 PCB pg-TEQ /Ldistribution bath m aterial tank 50-120m3 ferrous chloride iron dissolution tank 2HC l+Fe FeCl 2+H2 2FeC l 3+Fe 3FeC l 2 waste H C l steelmill H C l+FeC l 2 E tching waste liquid FeC l 2+FeC l 3 Printcircuitboard scrap iron steelsheet,press scrap density control filtration filtrate tank chlorination 2FeC l 2+C l 2 2FeC l 3 producttank ferric chloride (FeC l 3)manufacturing flow Cl 2gas Cu-recovery w ater treatm ent Etching liquid Figure 1 GC/MS chromatogram in contaminated FeCl3 Co-PXB: #126,#169,#189 monobromo substituted Figure 2 GC/MS chromatogram in contaminated FeCl3 Co-PXB: #126 PeCB, MBrTeCB, DiBrTrCB Figure 3 Fluorescent X-ray analysis of liquid samples (A) used etching waste, (B) FeCl2, (C) FeCl3 Figure 4 PBrDPE in strongly acidic solution in presence of HCl, FeCl 2 and CuCl 2 . Figure 5 TEQ contributions (%) of co-PCB in FeCl 3 Figure 6 Distributions of 3, 3’, 4, 4’, 5-PeXB in FeCl 3 . Figure 7 tetra-, penta-, hexa-, and hepta-XB. in FeCl3 Unique distributions of major PCB congeners from 3,3’-dichloro benzidine related sites. PCB concentrations in waste water treatment system. FeCl3 manufacturing process. Figure GC/MS chromatogram in contaminated FeCl3 (Co- PCB: #126) Figure GC/MS chromatogram in contaminated FeCl3 (Co- PCB: #169 FeCl3 manufacturing process and metal recovery process . FeCl 3 as coagul ant Coprecipitation involves remo val of two or more constituen ts by a precipitation reactio n. Coprecipitation of elemen t with Fe(OH)3 is an effective treatment process: FeCl 3 + 3H 2 O = Fe(OH) 3 + 3H + + 3Cl - FeCl 3 as etching liquid Ferric Chloride (FeCl3) is use d to etch away copper that is n't protected by the remainin g photoresist coating on the PC board (Printed circuit boa rd). To recover copper and ni ckel from a spent FeCl3 etchin g solution, these chemicals are recycled. Introduction In recent years it was found that several organic and inorganic food and feed add itives can be contaminated with PCDD/PCDF and other persistent organic pollutant s. One known example is the PCDD/PCDF contamination of chicken from contaminated ball clay used as food additives. Recently the EU have enacted a law with limits for PCDD/PCDF and PCB concentration for food and feed including food additives. C urrently inorganic food/feed additives are screened and evaluated in this respect in the EU. In Japan a research project was performed evaluating POPs in FeCl3. FeCl3 is used partly as food/feed additive but a much larger share of FeCl3 is used for purific ation of water. A common used waste water treatment step using FeCl3 is coagulati on following by a sedimentation step. A part of the FeCl3 is produced from recycl ed materials. One of the recycling processes use the Fe recovered from etching li quid of printed circuit board from and waste acids from steel mills. The aim of this study was to evaluate if the FeCl3 used for water treatment can b e contaminated with persistent organic pollutants. This first study revealed that FeCl3 can be highly contaminated with dioxin-like PCBs and chlorinated-brominated PXBs calling for further investigations and possibly actions on international lev el. Materials and Methods GC/MS analysis : The analysis was carried out using a HP 6890 gas chromatograph connected to a JMS-800D mass spectrometer (JEOL Ltd. Japan) operating at a resolution >10 000. Co-PCB, Co-PXB and PXDF were analyzed using HT8-PCB column. Temperature program used for congener specific separation of the PCB, PXB and PXDF on HT8- PCB column: 120C, 20C/min. to 180C, 2C/min. to 260C. 5C/min. to 300C, 5 min. isothermal. Monitoring ions for GC/MS analysis are listed in Table. Standards : Commercially-available native/labeled standards were obtained from CIL as authentic standard/mixtures for crosschecking the assignment. , 4’-bromo- 3, 3’, 4, 5-tetrachloro biphenyl was obtained from CIL for a PXB standard. Results and Conclusion - Some lots of FeCl3 produced and used for water purification were found to be highly contaminate d with PCBs (ng-TEQ/L) and chlorinated-brominate d PXBs. The contaminated lots of FeCl3 stem from a process using partly FeCl 3 as a recyling prod uct from etching of printed circuit boards. - As PCB contaminants mainly the toxic coplanar PCB congeners having dioxin-like properties and assigned TEQ values were found (#126 > #169 > #1 89). - In addition to the chlorinated PCBs also monob rominated-polychlorinated s of Co-PCB #126, #169 and #189 were detected in slightly lower concent rations (Figure 7). - Possible pathways for the formation of the PCB s are proposed: either from brominated flame re tardant contamination from the etching process (e.g. PBDE; Figure 4) or formation from certain aromatic organics forming PCBs during the chlori nation steps in the process of FeCl3. - The finding of highly dioxin-like PCB contamin ated FeCl3 used for waste purification is alarmi ng and need to be highlighted and investigated a s possible contamination source for drinking wat er and waste water sludge. Since the FeCl3 is us ed worldwide in water purification, investigatio ns should be initiated with an international per spective. HCl, FeCl 2 , CuCl 2 PBrDPE References 1. Grabda M, Oleszek-Kudlak S, Shibata E, Nakamura T, Organohalogen Comp 2006; 68:1983. B rPeC D F:417.7706,419.7679 PeBrB iphenyl:547.6268,549.6247 B rTeC DF :383.8096,385.8070 TeB r4M C B:501.6792,503.6771 B rTrC D F :349.8487,351.8460 T rB rD iCB :457.7297,459.7274 B rH xCB :437.7523,439.7496 D iB rTrC B :413.7800,415.777 B rPeC B :403.7913,405.7886 M B rTeC B :367.8329,369.8303 B rTeC B :367.8329,369.8303 13C -PeC B :337.920,339.9178 B rTrC B :333.8718,335.8694 PeC B :325.8805,327.8775 M onitoring ions ofPX B /PXD F NOON Cl Cl + H N Cl H N Cl HN Cl NHCl HSOHN Cl NHCl 2HCl Cl Cl HSOHCl PRODUCT Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl Cl OH Br Br Br Br Br Br O Br Br Br Br Br Br X X X X X X O X X X X X X X X X X X H Cl,FeCl 2, CuCl 2 (C l >> Br) OH Br Br Br Br Br Br O Br Br Br Br Br Br X X X X X X O X X X X X X X X X X X H Cl,FeCl 2, CuCl 2 (C l >> Br)

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Page 1: Distributions of 3,3 ’,4,4 ’,5-PeXB in FeCl 3 tetra-, penta-, hexa-, and hepta-XB. in FeCl 3 Etching liquid Etching waste Steel plant converter dust iron

3,3',4,4',5-PeXB

0

1

PCB-126 MonoBr DiBr

X

X

X

X

X

Br0Cl5

Br1Cl4

Br2Cl3

Distributions of 3,3’,4,4’,5-PeXB in FeCl3

tetra-XB penta-XB hexa-XB hepta-XB

3,3',4,4',5- 3,3',4,4',5,5'-

2,3,3',4,4',5,5'-3,3',4,4'-

X

X

X

X

X

X

X

X

X

X

X

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X

X

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X

X

X

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X

X

XX

XX

X

X

X

XX

X

X

X

X

X

X

X

X

X

tetra-, penta-, hexa-, and hepta-XB. in FeCl 3

32 36 40 44 48

0

71442Br2T3CB

32 36 40 44 48

0

1382993 BrT4CB

32 36 40 44 48

0

5678926

P5CB

32 36 40 44 48Retention Time (min)

0

1578810

13C-P5CB

#126

MBr-#126

DiBr-#126

#126#1

05

#114

#123

#118

32 36 40 44 48

0

71442Br2T3CB

32 36 40 44 48

0

1382993 BrT4CB

32 36 40 44 48

0

5678926

P5CB

32 36 40 44 48Retention Time (min)

0

1578810

13C-P5CB

#126

MBr-#126

DiBr-#126

#126#1

05

#114

#123

#118

28 32 36 40 44 48 52

0

160936

BrH6CB

28 32 36 40 44 48 52

0

2691689BrP5CB

28 32 36 40 44 48 52

0

2250853BrT4CB

28 32 36 40 44 48 52Retention Time (min)

1093

83433 BrT3CB

MBr-#126

MBr-#169

MBr-#189

28 32 36 40 44 48 52

0

160936

BrH6CB

28 32 36 40 44 48 52

0

2691689BrP5CB

28 32 36 40 44 48 52

0

2250853BrT4CB

28 32 36 40 44 48 52Retention Time (min)

1093

83433 BrT3CB

MBr-#126

MBr-#169

MBr-#189

X

X

X

X

X

X

X

X

X

X

X

X

X

X

X

X

X

X

X

X

X

X

X

X

X

X

XX

XX

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X

X

X

X

Etching liquid

Etching waste

Steel plantconverter dust

iron powder

Recycle plant

FeCl3

FeCl2

Cl2Etching plant

Fe

Cu

water treatment

Ni

Coagulant

printed circuit board etching plant

13C coPCB

PCB-126

Co-PCB

FeCl3STD

PeCB

13C coPCB

PCB-126

Co-PCB

FeCl3STD

PeCB

Co-PCB

0.0

100.0

#81

#77

#126

#169

TEQ(%)/L

Cl

Cl

Cl

Cl

Cl

Cl

Cl

Cl

Cl

Cl

Cl

Cl

ClCl

Cl

Cl

Cl

Cl

Cl

#169

#169

HxCB

FeCl3

STD

DETECTION OF POLY HALOGENATED BIPHENYLS IN THE FeCl3 MANUFACTURING PROCESS

Nakano T, Matsumura C, Tsurukawa M, and Moriguchi Y

Hyogo Prefectural Institute of Public Health and Environmental Sciences, 3-1-27 Yukihira-cho, Suma-ku, Kobe, 654-0037 Japan

(A)

(B)

(C)

Fe

Cu

Cu

Br

Pb

Fe

Fe

Zn

Ni

Mn Cr

Fe

Zn Ni

Mn

Fe F

e

Zn Ni

Mn

CuCuP

b Cr

(A)

(B)

(C)

Fe

Cu

Cu

Br

Pb

Fe

Fe

Zn

Ni

Mn Cr

Fe

Zn Ni

Mn

Fe F

e

Zn Ni

Mn

CuCuP

b Cr

Etching

FeCl2

FeCl3

raw w

ater

warm

ing b

ath

con

tact oxid

ation

nitrificatio

n

den

itrification

re-aeratio

n

rapid

ly-stirrin

g

slowly

-stirring

coag

ulatio

n bath

neu

tralization

sterilization

bath

0

40

80

120

160

effluen

tb

ath

H3PO4

NaOHH2SO4

NaOH

NaOH

MeOH

FeCl3

NaOHH2SO4

NaOHH2SO4

sodium hypochlorite

NaClO

[Al2(OH)nCl6-n]m

12.5m3 224m3

24m3

PCB (pg-TEQ/L)

distrib

utio

n

bath

material

tank

50-120m3

ferrous chlorideiron dissolution tank2HCl+Fe FeCl2+H2

2FeCl3+Fe 3FeCl2

waste HClsteel mill

HCl+FeCl2

Etching waste liquidFeCl2+FeCl3

Print circuit board

scrap ironsteel sheet , press scrap

den

sity con

trol

filtration

filtrate tank

chlorination2FeCl2+Cl2 2FeCl3

pro

du

ct tank

ferric chloride (FeCl3) manufacturing flow

Cl2 gas

Cu

-recovery

water treatment

Etching liquid

Figure 1 GC/MS chromatogram in contaminated FeCl3

Co-PXB: #126,#169,#189 ( monobromo substituted )

Figure 2 GC/MS chromatogram in contaminated FeCl3

Co-PXB: #126 ( PeCB, MBrTeCB, DiBrTrCB )

Figure 3 Fluorescent X-ray analysis of liquid samples (A) used etching waste, (B) FeCl2, (C) FeCl3

Figure 4 PBrDPE in strongly acidic solution in presence of HCl, FeCl2 and CuCl2.

Figure 5 TEQ contributions (%) of co-PCB in FeCl3

Figure 6 Distributions of 3, 3’, 4, 4’, 5-PeXB in FeCl3. Figure 7 tetra-, penta-, hexa-, and hepta-XB. in FeCl3

Unique distributions of major PCB congeners from 3,3’-dichloro benzidine related sites.

PCB concentrations in waste water treatment system.

FeCl3 manufacturing process.

Figure GC/MS chromatogram in contaminated FeCl3 (Co-PCB: #126)

Figure GC/MS chromatogram in contaminated FeCl3 (Co-PCB: #169 )

FeCl3 manufacturing process and metal recovery process .

FeCl3 as coagulant

Coprecipitation involves removal of two or more constituents by a precipitation reaction. Coprecipitation of element with Fe(OH)3 is an effective treatment process:

FeCl3 + 3H2O = Fe(OH)3 + 3H+ + 3Cl-

FeCl3 as etching liquid

Ferric Chloride (FeCl3) is used to etch away copper that isn't protected by the remaining photoresist coating on the PC board (Printed circuit board). To recover copper and nickel from a spent FeCl3 etching solution, these chemicals are recycled.

Introduction

In recent years it was found that several organic and inorganic food and feed additives can be contaminated with PCDD/PCDF and other persistent organic pollutants. One known example is the PCDD/PCDF contamination of chicken from contaminated ball clay used as food additives. Recently the EU have enacted a law with limits for PCDD/PCDF and PCB concentration for food and feed including food additives. Currently inorganic food/feed additives are screened and evaluated in this respect in the EU. In Japan a research project was performed evaluating POPs in FeCl3. FeCl3 is used partly as food/feed additive but a much larger share of FeCl3 is used for purification of water. A common used waste water treatment step using FeCl3 is coagulation following by a sedimentation step. A part of the FeCl3 is produced from recycled materials. One of the recycling processes use the Fe recovered from etching liquid of printed circuit board from and waste acids from steel mills.The aim of this study was to evaluate if the FeCl3 used for water treatment can be contaminated with persistent organic pollutants. This first study revealed that FeCl3 can be highly contaminated with dioxin-like PCBs and chlorinated-brominated PXBs calling for further investigations and possibly actions on international level.

Materials and MethodsGC/MS analysis : The analysis was carried out using a HP 6890 gas chromatograph connected to a JMS-800D mass spectrometer (JEOL Ltd. Japan) operating at a resolution >10 000. Co-PCB, Co-PXB and PXDF were analyzed using HT8-PCB column. Temperature program used for congener specific separation of the PCB, PXB and PXDF on HT8-PCB column: 120C, 20C/min. to 180C, 2C/min. to 260C. 5C/min. to 300C, 5 min. isothermal. Monitoring ions for GC/MS analysis are listed in Table.

Standards: Commercially-available native/labeled standards were obtained from CIL as authentic standard/mixtures for crosschecking the assignment. , 4’-bromo- 3, 3’, 4, 5-tetrachloro biphenyl was obtained from CIL for a PXB standard.

Results and Conclusion

- Some lots of FeCl3 produced and used for water purification were found to be highly contaminated with PCBs (ng-TEQ/L) and chlorinated-brominated PXBs. The contaminated lots of FeCl3 stem from a process using partly FeCl3 as a recyling product from etching of printed circuit boards.

- As PCB contaminants mainly the toxic coplanar PCB congeners having dioxin-like properties and assigned TEQ values were found (#126 > #169 > #189).

- In addition to the chlorinated PCBs also monobrominated-polychlorinated s of Co-PCB #126, #169 and #189 were detected in slightly lower concentrations (Figure 7).

- Possible pathways for the formation of the PCBs are proposed: either from brominated flame retardant contamination from the etching process (e.g. PBDE; Figure 4) or formation from certain aromatic organics forming PCBs during the chlorination steps in the process of FeCl3.

- The finding of highly dioxin-like PCB contaminated FeCl3 used for waste purification is alarming and need to be highlighted and investigated as possible contamination source for drinking water and waste water sludge. Since the FeCl3 is used worldwide in water purification, investigations should be initiated with an international perspective.

HCl, FeCl2, CuCl2 PBrDPE

References1. Grabda M, Oleszek-Kudlak S, Shibata E, Nakamura T, Organohalogen Comp 2006; 68:1983.

BrPeCDF: 417.7706, 419.7679PeBrBiphenyl: 547.6268, 549.6247

BrTeCDF : 383.8096, 385.8070TeBr4MCB: 501.6792, 503.6771

BrTrCDF : 349.8487, 351.8460TrBrDiCB: 457.7297, 459.7274

BrHxCB: 437.7523, 439.7496DiBrTrCB : 413.7800, 415.777

BrPeCB: 403.7913, 405.7886MBrTeCB : 367.8329, 369.8303

BrTeCB: 367.8329, 369.830313C-PeCB: 337.920, 339.9178

BrTrCB: 333.8718, 335.8694PeCB: 325.8805, 327.8775

Monitoring ions of PXB/PXDF

NO2 O2N

Cl Cl

+ HN

Cl

HN

Cl

H2N

Cl

NH2

Cl

H2SO4

H2N

Cl

NH2

Cl

2HCl

Cl Cl

H2SO4

HCl

PRODUCT

Cl Cl

Cl Cl

Cl

Cl Cl

Cl

ClCl

Cl Cl

Cl

Cl Cl

Cl

Cl

Cl Cl

Cl

Cl

Cl Cl

Cl Cl

OH

Br

Br

Br

Br

Br

Br

O

Br

Br

Br

Br

Br

Br

X

X

X

X

X

X

O

X

X

X

X

X

X X

X

X

X

X

HCl, FeCl2, CuCl2( Cl >> Br )

OH

Br

Br

Br

Br

Br

Br

O

Br

Br

Br

Br

Br

Br

X

X

X

X

X

X

O

X

X

X

X

X

X X

X

X

X

X

HCl, FeCl2, CuCl2( Cl >> Br )