pdp kruger road, secunda, 2302 waste generating · applicant sasol south africa (ltd) waste stream...
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Page 1 of 6
RISK ASSESSMENT IN TERMS OF REGULATION 8 OF THE WASTE EXCLUSION REGULATIONS
APPLICANT Sasol South Africa (Ltd)
WASTE STREAM OR PORTION OF A WASTE STREAM
Fresh coarse ash
BENEFICIAL USE/S
Sasol Fresh coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Brickmaking (b) Block making (c) Production of cement
WASTE GENERATING FACILITY OR FACILITIES
PHYSICAL ADDRESS OF FACILITY OR FACILITIES
PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY OR FACILITIES
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
CONTACT PERSON
NAME Kashmira Doelab (Secunda Synfuels Operations (SSO): Acting Manager SHE: Waste)
ADDRESS Private Bag X1000 Secunda
2302
EMAIL ADDRESS [email protected]
TELEPHONE
+27 17 610 7143
+27 72 580 9842
Page 2 of 6
* DETAILED DESCRIPTION OF WASTE GENERATING PROCESS
Secunda Synfuels Operations Process: The sources of ash generated at Secunda Synfuels Operations are the Steam plant and Gasification plant where synthesis gas and steam are generated respectively.
Ash from the gasification process is made up of an 80 % coarse ash fraction, which is transported to the coarse ash heaps via conveyor belts, and a 20 % fine ash fraction which is transported to the fine ash dams in a slurry form by means of pumping.
Ash from the combustion process is made up of 86.4 % fine ash, which is transported to the fine ash dams together with the gasification fine ash fraction. The remaining 13.6% coarse ash is transported to the ash heaps together with the gasification coarse ash fraction.
PRODUCTION PROCESS FLOW CHART ATTACHED
YES X NO
IDENTIFICATION OF HAZARDS
WASTE CLASSIFICATION
HAZARDOUS GENERAL
X
IF WASTE IS HAZARDOUS LIST THE HAZARDS OF THE WASTE
Health hazards due to the presence of lime (CaO) and SiO2 occurring as quartz
*A process flow chart must be attached to the process description
Page 3 of 6
RISK ASSESSEMENT WITHOUT MITIGATION
Activity Risk Description
Environmental receptors
Impact Assessment of the risk Significance
Probability Magnitude
Duration Scale
1. Loading of ash onto trucks
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
2. Transportation of ash
Loss of containment of ash
Air Dust generation along
transportation route Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Local: 2
Inherent: 25, low environmental significance
Land Load of ash deposited on
land in the vicinity of the road Land pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Load of ash deposited in
water body in the vicinity of the road
Water pollution
Inherent: Medium probability: 3
Inherent: Moderate: 6
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 27, low environmental significance
3. Off-loading of ash Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
4. Storage of ash Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Highly probable: 4
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 16, low environmental significance
Land Ash carried by run-off
deposited on land in the vicinity of the ash storage area
Land degradation
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Water Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
5. Handling of ash (i.e. screening, crushing, blending etc.)
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor:2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
Page 4 of 6
a. Brickmaking; b. Block making; c. Production of
cement.
The point at which coal ash enters the production process of bricks, blocks and cement to the actual products is outside the scope of this risk assessment. The incorporation of coal ash into these existing production processes is matured. The quality of the products from these processes is regulated by relevant standards.
6. Disposal of ash and ash containing products
Loss of containment of ash
Air Localised dust generation Air pollution
Residual: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Land Load of ash disposed illegally
on land Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Illegally disposed ash
reaching water body in the vicinity of the dumping area
Water pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
7. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 12, low environmental significance
Land Ash carried by run-off
deposited on land in the vicinity of the ash storage area
Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
Page 5 of 6
The following factors and criteria must be used to assess the impacts of the activities:
Criteria MAGNITUDE (Severity) DURATION
10 - Very high 5 – Permanent (longer than 10 years) 8 – High 4 - Long-term (5 to 10 years) 6 – Moderate 3 - Medium-term (12 months to 5 years) 4 – Low 2 - Short-term (0 to 12 months) 2 – Minor 1 – Immediate
SCALE PROBABILITY (Likelihood) 5 – International 5 - Definite 4 – National 4 - Highly probable 3 – Regional 3 - Medium probability 2 – Local 2 - Low probability 1 - Site only 1 – Improbable 0 – None 0 – None
Magnitude Magnitude measures the size of the impact
Duration Duration refers to the lifetime of the impact i.e. how long it will last
Scale The scale refers to the extent of the impact.
Probability The probability refers to the chance of impact to occur. The potential impact could be most likely to occur, unlikely, etc. Assessment of Significance of impact Significance rating of the potential impacts illustrates the importance of the impact itself. The size of area affected by pollution may be extremely high but the significance of this effect is dependent on the concentration or level of pollution in that area. In order to determine the significance of impact, the following method was used: Significance Points (SP) = (Magnitude + Duration + Scale) x Probability The values of SP are then ranged as follows:
Rating Description
SP >60 Indicates high environmental significance
An impact which could influence the decision about whether or not to proceed with the activities regardless of any possible mitigation.
SP 30 – 60 Indicates moderate environmental significance
An impact or benefit which is sufficiently important to require management and which could have an influence on the decision unless it is mitigated.
SP <30 Indicates low environmental significance
Impacts with little real effect and which will not have an influence on or require modification of the activities.
+ Positive impact An impact that is likely to result in positive consequences/effects
Page 6 of 6
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not Authorised( provide reasons)
Reference Number
Page 1 of 7
RISK ASSESSMENT IN TERMS OF REGULATION 8 OF THE WASTE EXCLUSION REGULATIONS
APPLICANT Sasol South Africa (Ltd)
WASTE STREAM OR PORTION OF A WASTE STREAM
Fresh coarse ash
BENEFICIAL USE/S
Sasol Fresh coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Road construction (b) Foundations (c) Backfill in mine workings (d) Landfill capping
WASTE GENERATING FACILITY OR FACILITIES
PHYSICAL ADDRESS OF FACILITY OR FACILITIES
PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY OR FACILITIES
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
CONTACT PERSON
NAME Kashmira Doelab (Secunda Synfuels Operations (SSO): Acting Manager SHE: Waste)
ADDRESS Private Bag X1000 Secunda
2302
EMAIL ADDRESS [email protected]
TELEPHONE
+27 17 610 7143
+27 72 580 9842
Page 2 of 7
* DETAILED DESCRIPTION OF WASTE GENERATING PROCESS
Secunda Synfuels Operations Process: The sources of ash generated at Secunda Synfuels Operations are the Steam plant and Gasification plant where synthesis gas and steam are generated respectively.
Ash from the gasification process is made up of an 80 % coarse ash fraction, which is transported to the coarse ash heaps via conveyor belts, and a 20 % fine ash fraction which is transported to the fine ash dams in a slurry form by means of pumping.
Ash from the combustion process is made up of 86.4 % fine ash, which is transported to the fine ash dams together with the gasification fine ash fraction. The remaining 13.6% coarse ash is transported to the ash heaps together with the gasification coarse ash fraction.
PRODUCTION PROCESS FLOW CHART ATTACHED
YES X NO
IDENTIFICATION OF HAZARDS
WASTE CLASSIFICATION
HAZARDOUS GENERAL
X IF WASTE IS HAZARDOUS LIST THE HAZARDS OF THE WASTE
Health hazards due to the presence of lime (CaO) and SiO2 occurring as quartz
*A process flow chart must be attached to the process description
Page 3 of 7
RISK ASSESSEMENT WITHOUT MITIGATION
Activity Risk Description
Environmental receptors
Impact Assessment of the risk
Probability Magnitude
Duration Scale Significance
1. Loading of ash onto trucks
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
2. Transportation of ash
Loss of containment of ash
Air Dust generation along
transportation route Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Local: 2
Inherent: 25, low environmental significance
Land Load of ash deposited on
land in the vicinity of the road Land pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Load of ash deposited in
water body in the vicinity of the road
Water pollution
Inherent: Medium probability: 3
Inherent: Moderate: 6
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 27, low environmental significance
3. Off-loading of ash Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
4. Storage of ash Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Highly probable: 4
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 16, low environmental significance
Land Ash carried by run-off
deposited on land in the vicinity of the ash storage area
Land degradation
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Water Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
Page 4 of 7
Activity Risk Description
Environmental receptors
Impact Assessment of the risk
Probability Magnitude
Duration Scale Significance
5. Handling of ash (i.e. screening, crushing, blending etc.)
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor:2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
6. Incorporation of coal ash in construction land applications
a. Road construction;
b. Foundations; c. Backfill in mine
workings; d. Landfill capping.
Improper incorporation of ash in construction land applications
Air Localised dust generation Air pollution
Inherent: Highly probable: 4
Inherent: Minor: 2
Inherent: Medium term (12 months to 5 years): 3
Inherent: Site only: 1
Inherent: 24, low environmental significance
Land Land degradation Inherent:
Low probability: 2
Inherent: Low: 4
Inherent: Long term (5 to 10 years): 4
Inherent: Site only: 1
Inherent: 18, low environmental significance
Water Ash carried by run-off and
deposited into surface and ground water sources (increase in Total Suspended Solids TSS)
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Medium term (12 months to 5 years): 3
Inherent: Site only: 1
Inherent: 18, low environmental significance
7. Disposal of ash and ash containing mixtures
Loss of containment of ash
Air Localised dust generation Air pollution
Residual: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Land Load of ash disposed illegally
on land Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Illegally disposed ash
reaching water body in the vicinity of the dumping area
Water pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
8. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 12, low environmental significance
Land Ash carried by run-off
deposited on land in the vicinity of the ash storage area
Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Page 5 of 7
Activity Risk Description
Environmental receptors
Impact Assessment of the risk
Probability Magnitude
Duration Scale Significance
Water Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
Page 6 of 7
The following factors and criteria must be used to assess the impacts of the activities:
Criteria
MAGNITUDE (Severity) DURATION 10 - Very high 5 – Permanent (longer than 10 years) 8 – High 4 - Long-term (5 to 10 years) 6 – Moderate 3 - Medium-term (12 months to 5 years) 4 – Low 2 - Short-term (0 to 12 months) 2 – Minor 1 – Immediate
SCALE PROBABILITY (Likelihood) 5 – International 5 - Definite 4 – National 4 - Highly probable 3 – Regional 3 - Medium probability 2 – Local 2 - Low probability 1 - Site only 1 – Improbable 0 – None 0 – None
Magnitude Magnitude measures the size of the impact
Duration Duration refers to the lifetime of the impact i.e. how long it will last
Scale The scale refers to the extent of the impact.
Probability The probability refers to the chance of impact to occur. The potential impact could be most likely to occur, unlikely, etc. Assessment of Significance of impact Significance rating of the potential impacts illustrates the importance of the impact itself. The size of area affected by pollution may be extremely high but the significance of this effect is dependent on the concentration or level of pollution in that area. In order to determine the significance of impact, the following method was used: Significance Points (SP) = (Magnitude + Duration + Scale) x Probability The values of SP are then ranged as follows:
Rating Description
SP >60 Indicates high environmental significance
An impact which could influence the decision about whether or not to proceed with the activities regardless of any possible mitigation.
SP 30 – 60 Indicates moderate environmental significance
An impact or benefit which is sufficiently important to require management and which could have an influence on the decision unless it is mitigated.
SP <30 Indicates low environmental significance
Impacts with little real effect and which will not have an influence on or require modification of the activities.
+ Positive impact An impact that is likely to result in positive consequences/effects
Page 7 of 7
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not Authorised( provide reasons)
Reference Number
Page 1 of 7
RISK ASSESSMENT IN TERMS OF REGULATION 8 OF THE WASTE EXCLUSION REGULATIONS
APPLICANT Sasol South Africa (Ltd)
WASTE STREAM OR PORTION OF A WASTE STREAM
Fresh coarse ash
BENEFICIAL USE/S
Sasol Fresh coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Inorganic fertilizer; (b) Soil ameliorant and conditioner; and (c) Bulking agent for composting.
WASTE GENERATING FACILITY OR FACILITIES
PHYSICAL ADDRESS OF FACILITY OR FACILITIES
PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY OR FACILITIES
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
CONTACT PERSON
NAME Kashmira Doelab (Secunda Synfuels Operations (SSO): Manager SHE: Waste)
ADDRESS Private Bag X1000 Secunda
2302
EMAIL ADDRESS [email protected]
TELEPHONE
+27 17 610 7143
+27 72 580 9842
Page 2 of 7
* DETAILED DESCRIPTION OF WASTE GENERATING PROCESS
Secunda Synfuels Operations Process: The sources of ash generated at Secunda Synfuels Operations are the Steam plant and Gasification plant where synthesis gas and steam are generated respectively.
Ash from the gasification process is made up of an 80 % coarse ash fraction, which is transported to the coarse ash heaps via conveyor belts, and a 20 % fine ash fraction which is transported to the fine ash dams in a slurry form by means of pumping.
Ash from the combustion process is made up of 86.4 % fine ash, which is transported to the fine ash dams together with the gasification fine ash fraction. The remaining 13.6% coarse ash is transported to the ash heaps together with the gasification coarse ash fraction.
PRODUCTION PROCESS FLOW CHART ATTACHED
YES X NO
IDENTIFICATION OF HAZARDS
WASTE CLASSIFICATION
HAZARDOUS GENERAL
X IF WASTE IS HAZARDOUS LIST THE HAZARDS OF THE WASTE
Health hazards due to the presence of lime (CaO) and SiO2 occurring as quartz
*A process flow chart must be attached to the process description
Page 3 of 7
RISK ASSESSEMENT WITHOUT MITIGATION
Activity Risk Description
Environmental receptors
Impact Assessment of the risk
Probability Magnitude
Duration Scale Significance
1. Loading of ash onto trucks
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
2. Transportation of ash
Loss of containment of ash
Air Dust generation along
transportation route Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Local: 2
Inherent: 25, low environmental significance
Land Load of ash deposited on
land in the vicinity of the road Land pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Load of ash deposited in
water body in the vicinity of the road
Water pollution
Inherent: Medium probability: 3
Inherent: Moderate: 6
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 27, low environmental significance
3. Off-loading of ash Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
4. Storage of ash Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Highly probable: 4
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 16, low environmental significance
Land Ash carried by run-off
deposited on land in the vicinity of the ash storage area
Land degradation
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Water Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
Page 4 of 7
Activity Risk Description
Environmental receptors
Impact Assessment of the risk
Probability Magnitude
Duration Scale Significance
5. Handling of ash (i.e. screening, crushing, blending etc.)
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor:2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
6. Incorporation of coal ash in agricultural land applications a. Inorganic
fertilizer; b. Soil ameliorant
and conditioner; and
c. Bulking agent for composting.
Improper incorporation of ash in agricultural land applications
Air Localised dust generation Air pollution
Inherent: Highly probable: 4
Inherent: Minor: 2
Inherent: Medium term (12 months to 5 years): 3
Inherent: Site only: 1
Inherent: 24, low environmental significance
Land Land degradation Inherent:
Low probability: 2
Inherent: Low: 4
Inherent: Long term (5 to 10 years): 4
Inherent: Site only: 1
Inherent: 18, low environmental significance
Water Ash carried by run-off and
deposited into surface and ground water sources (increase in Total Suspended Solids TSS)
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Medium term (12 months to 5 years): 3
Inherent: Site only: 1
Inherent: 18, low environmental significance
7. Disposal of ash and ash containing mixtures
Loss of containment of ash
Air Localised dust generation Air pollution
Residual: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Land Load of ash disposed illegally
on land Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Illegally disposed ash
reaching water body in the vicinity of the dumping area
Water pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
8. Residual ash stockpiled after closure, decommissioning or change of
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 12, low environmental significance
Land Ash carried by run-off
deposited on land in the vicinity of the ash storage area
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Page 5 of 7
Activity Risk Description
Environmental receptors
Impact Assessment of the risk
Probability Magnitude
Duration Scale Significance
ownership of user facility
Land degradation
Water Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
Page 6 of 7
The following factors and criteria must be used to assess the impacts of the activities:
Criteria MAGNITUDE (Severity) DURATION
10 - Very high 5 – Permanent (longer than 10 years) 8 – High 4 - Long-term (5 to 10 years) 6 – Moderate 3 - Medium-term (12 months to 5 years) 4 – Low 2 - Short-term (0 to 12 months) 2 – Minor 1 – Immediate
SCALE PROBABILITY (Likelihood) 5 – International 5 - Definite 4 – National 4 - Highly probable 3 – Regional 3 - Medium probability 2 – Local 2 - Low probability 1 - Site only 1 – Improbable 0 – None 0 – None
Magnitude Magnitude measures the size of the impact
Duration Duration refers to the lifetime of the impact i.e. how long it will last
Scale The scale refers to the extent of the impact.
Probability The probability refers to the chance of impact to occur. The potential impact could be most likely to occur, unlikely, etc. Assessment of Significance of impact Significance rating of the potential impacts illustrates the importance of the impact itself. The size of area affected by pollution may be extremely high but the significance of this effect is dependent on the concentration or level of pollution in that area. In order to determine the significance of impact, the following method was used: Significance Points (SP) = (Magnitude + Duration + Scale) x Probability The values of SP are then ranged as follows:
Rating Description
SP >60 Indicates high environmental significance
An impact which could influence the decision about whether or not to proceed with the activities regardless of any possible mitigation.
SP 30 – 60 Indicates moderate environmental significance
An impact or benefit which is sufficiently important to require management and which could have an influence on the decision unless it is mitigated.
SP <30 Indicates low environmental significance
Impacts with little real effect and which will not have an influence on or require modification of the activities.
+ Positive impact An impact that is likely to result in positive consequences/effects
Page 7 of 7
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not Authorised( provide reasons)
Reference Number
Page 1 of 6
RISK ASSESSMENT IN TERMS OF REGULATION 8 OF THE WASTE EXCLUSION REGULATIONS
APPLICANT Sasol South Africa (Ltd)
WASTE STREAM OR PORTION OF A WASTE STREAM
Fresh coarse ash
BENEFICIAL USE/S
Sasol Fresh coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Aggregate
WASTE GENERATING FACILITY OR FACILITIES
PHYSICAL ADDRESS OF FACILITY OR FACILITIES
PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY OR FACILITIES
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
CONTACT PERSON
NAME Kashmira Doelab (Secunda Synfuels Operations (SSO): Acting Manager SHE: Waste)
ADDRESS Private Bag X1000 Secunda 2302
EMAIL ADDRESS [email protected]
TELEPHONE
+27 17 610 7143 +27 72 580 9842
Page 2 of 6
* DETAILED DESCRIPTION OF WASTE GENERATING PROCESS
Secunda Synfuels Operations Process: The sources of ash generated at Secunda Synfuels Operations are the Steam plant and Gasification plant where synthesis gas and steam are generated respectively.
Ash from the gasification process is made up of an 80 % coarse ash fraction, which is transported to the coarse ash heaps via conveyor belts, and a 20 % fine ash fraction which is transported to the fine ash dams in a slurry form by means of pumping.
Ash from the combustion process is made up of 86.4 % fine ash, which is transported to the fine ash dams together with the gasification fine ash fraction. The remaining 13.6% coarse ash is transported to the ash heaps together with the gasification coarse ash fraction.
PRODUCTION PROCESS FLOW CHART ATTACHED
YES X NO
IDENTIFICATION OF HAZARDS
WASTE CLASSIFICATION
HAZARDOUS GENERAL
X
IF WASTE IS HAZARDOUS LIST THE HAZARDS OF THE WASTE
Health hazards due to the presence of lime (CaO) and SiO2 occurring as quartz
*A process flow chart must be attached to the process description
Page 3 of 6
RISK ASSESSEMENT WITHOUT MITIGATION
Activity Risk Description
Environmental receptors
Impact Assessment of the risk Significance
Probability Magnitude
Duration Scale
1. Loading of ash onto trucks
Loss of containment of ash
Air • Localised dust generation • Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
2. Transportation of ash
Loss of containment of ash
Air • Dust generation along
transportation route • Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Local: 2
Inherent: 25, low environmental significance
Land • Load of ash deposited on
land in the vicinity of the road • Land pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water • Load of ash deposited in
water body in the vicinity of the road
• Water pollution
Inherent: Medium probability: 3
Inherent: Moderate: 6
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 27, low environmental significance
3. Off-loading of ash Loss of containment of ash
Air • Localised dust generation • Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
4. Storage of ash Loss of containment of ash
Air • Localised dust generation • Air pollution
Inherent: Highly probable: 4
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 16, low environmental significance
Land • Ash carried by run-off
deposited on land in the vicinity of the ash storage area
• Land degradation
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Water • Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
5. Handling of ash which includes the production of
Loss of containment of ash
Air • Localised dust generation • Air pollution
Inherent: Definite: 5
Inherent: Minor:2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
Page 4 of 6
aggregate (i.e. screening, crushing, blending etc.)
6. Disposal of ash and ash containing products
Loss of containment of ash
Air • Localised dust generation • Air pollution
Residual: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Land • Load of ash disposed illegally
on land • Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water • Illegally disposed ash
reaching water body in the vicinity of the dumping area
• Water pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
7. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Air • Localised dust generation • Air pollution
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 12, low environmental significance
Land • Ash carried by run-off
deposited on land in the vicinity of the ash storage area
• Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water • Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
Page 5 of 6
The following factors and criteria must be used to assess the impacts of the activities:
Criteria MAGNITUDE (Severity) DURATION
10 - Very high 5 – Permanent (longer than 10 years) 8 – High 4 - Long-term (5 to 10 years) 6 – Moderate 3 - Medium-term (12 months to 5 years) 4 – Low 2 - Short-term (0 to 12 months) 2 – Minor 1 – Immediate
SCALE PROBABILITY (Likelihood) 5 – International 5 - Definite 4 – National 4 - Highly probable 3 – Regional 3 - Medium probability 2 – Local 2 - Low probability 1 - Site only 1 – Improbable 0 – None 0 – None
Magnitude Magnitude measures the size of the impact
Duration Duration refers to the lifetime of the impact i.e. how long it will last
Scale The scale refers to the extent of the impact.
Probability The probability refers to the chance of impact to occur. The potential impact could be most likely to occur, unlikely, etc. Assessment of Significance of impact Significance rating of the potential impacts illustrates the importance of the impact itself. The size of area affected by pollution may be extremely high but the significance of this effect is dependent on the concentration or level of pollution in that area. In order to determine the significance of impact, the following method was used: Significance Points (SP) = (Magnitude + Duration + Scale) x Probability The values of SP are then ranged as follows:
Rating Description
SP >60 Indicates high environmental significance
An impact which could influence the decision about whether or not to proceed with the activities regardless of any possible mitigation.
SP 30 – 60 Indicates moderate environmental significance
An impact or benefit which is sufficiently important to require management and which could have an influence on the decision unless it is mitigated.
SP <30 Indicates low environmental significance
Impacts with little real effect and which will not have an influence on or require modification of the activities.
+ Positive impact An impact that is likely to result in positive consequences/effects
Page 6 of 6
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not Authorised( provide reasons)
Reference Number
Page 1 of 6
RISK ASSESSMENT IN TERMS OF REGULATION 8 OF THE WASTE EXCLUSION REGULATIONS
APPLICANT Sasol South Africa (Ltd)
WASTE STREAM OR PORTION OF A WASTE STREAM
Weathered coarse ash
BENEFICIAL USE/S
Sasol Weathered coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Brickmaking (b) Block making (c) Production of cement
WASTE GENERATING FACILITY OR FACILITIES
PHYSICAL ADDRESS OF FACILITY OR FACILITIES
PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY OR FACILITIES
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
CONTACT PERSON
NAME Kashmira Doelab (Secunda Synfuels Operations (SSO): Acting Manager SHE: Waste)
ADDRESS Private Bag X1000 Secunda
2302
EMAIL ADDRESS [email protected]
TELEPHONE
+27 17 610 7143
+27 72 580 9842
Page 2 of 6
* DETAILED DESCRIPTION OF WASTE GENERATING PROCESS
Secunda Synfuels Operations Process: The sources of ash generated at Secunda Synfuels Operations are the Steam plant and Gasification plant where synthesis gas and steam are generated respectively.
Ash from the gasification process is made up of an 80 % coarse ash fraction, which is transported to the coarse ash heaps via conveyor belts, and a 20 % fine ash fraction which is transported to the fine ash dams in a slurry form by means of pumping.
Ash from the combustion process is made up of 86.4 % fine ash, which is transported to the fine ash dams together with the gasification fine ash fraction. The remaining 13.6% coarse ash is transported to the ash heaps together with the gasification coarse ash fraction.
PRODUCTION PROCESS FLOW CHART ATTACHED
YES X NO
IDENTIFICATION OF HAZARDS
WASTE CLASSIFICATION
HAZARDOUS GENERAL
X IF WASTE IS HAZARDOUS LIST THE HAZARDS OF THE WASTE
Health hazards due to the presence of lime (CaO) and SiO2 occurring as quartz
*A process flow chart must be attached to the process description
Page 3 of 6
RISK ASSESSEMENT WITHOUT MITIGATION
Activity Risk Description
Environmental receptors
Impact Assessment of the risk Significance
Probability Magnitude
Duration Scale
1. Loading of ash onto trucks
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
2. Transportation of ash
Loss of containment of ash
Air Dust generation along
transportation route Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Local: 2
Inherent: 25, low environmental significance
Land Load of ash deposited on
land in the vicinity of the road Land pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Load of ash deposited in
water body in the vicinity of the road
Water pollution
Inherent: Medium probability: 3
Inherent: Moderate: 6
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 27, low environmental significance
3. Off-loading of ash Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
4. Storage of ash Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Highly probable: 4
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 16, low environmental significance
Land Ash carried by run-off
deposited on land in the vicinity of the ash storage area
Land degradation
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Water Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
5. Handling of ash (i.e. screening, crushing, blending etc.)
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor:2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
Page 4 of 6
a. Brickmaking; b. Block making; c. Production of
cement.
The point at which coal ash enters the production process of bricks, blocks and cement to the actual products is outside the scope of this risk assessment. The incorporation of coal ash into these existing production processes is matured. The quality of the products from these processes is regulated by relevant standards.
6. Disposal of ash and ash containing products
Loss of containment of ash
Air Localised dust generation Air pollution
Residual: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Land Load of ash disposed illegally
on land Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Illegally disposed ash
reaching water body in the vicinity of the dumping area
Water pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
7. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 12, low environmental significance
Land Ash carried by run-off
deposited on land in the vicinity of the ash storage area
Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
Page 5 of 6
The following factors and criteria must be used to assess the impacts of the activities:
Criteria MAGNITUDE (Severity) DURATION
10 - Very high 5 – Permanent (longer than 10 years) 8 – High 4 - Long-term (5 to 10 years) 6 – Moderate 3 - Medium-term (12 months to 5 years) 4 – Low 2 - Short-term (0 to 12 months) 2 – Minor 1 – Immediate
SCALE PROBABILITY (Likelihood) 5 – International 5 - Definite 4 – National 4 - Highly probable 3 – Regional 3 - Medium probability 2 – Local 2 - Low probability 1 - Site only 1 – Improbable 0 – None 0 – None
Magnitude Magnitude measures the size of the impact
Duration Duration refers to the lifetime of the impact i.e. how long it will last
Scale The scale refers to the extent of the impact.
Probability The probability refers to the chance of impact to occur. The potential impact could be most likely to occur, unlikely, etc. Assessment of Significance of impact Significance rating of the potential impacts illustrates the importance of the impact itself. The size of area affected by pollution may be extremely high but the significance of this effect is dependent on the concentration or level of pollution in that area. In order to determine the significance of impact, the following method was used: Significance Points (SP) = (Magnitude + Duration + Scale) x Probability The values of SP are then ranged as follows:
Rating Description
SP >60 Indicates high environmental significance
An impact which could influence the decision about whether or not to proceed with the activities regardless of any possible mitigation.
SP 30 – 60 Indicates moderate environmental significance
An impact or benefit which is sufficiently important to require management and which could have an influence on the decision unless it is mitigated.
SP <30 Indicates low environmental significance
Impacts with little real effect and which will not have an influence on or require modification of the activities.
+ Positive impact An impact that is likely to result in positive consequences/effects
Page 6 of 6
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not Authorised( provide reasons)
Reference Number
Page 1 of 7
RISK ASSESSMENT IN TERMS OF REGULATION 8 OF THE WASTE EXCLUSION REGULATIONS
APPLICANT Sasol South Africa (Ltd)
WASTE STREAM OR PORTION OF A WASTE STREAM
Weathered coarse ash
BENEFICIAL USE/S
Sasol Weathered coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Road construction; (b) Foundations; (c) Backfill in mine workings; (d) Landfill capping.
WASTE GENERATING FACILITY OR FACILITIES
PHYSICAL ADDRESS OF FACILITY OR FACILITIES
PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY OR FACILITIES
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
CONTACT PERSON
NAME Kashmira Doelab (Secunda Synfuels Operations (SSO): Acting Manager SHE: Waste)
ADDRESS Private Bag X1000 Secunda
2302
EMAIL ADDRESS [email protected]
TELEPHONE
+27 17 610 7143
+27 72 580 9842
Page 2 of 7
* DETAILED DESCRIPTION OF WASTE GENERATING PROCESS
Secunda Synfuels Operations Process: The sources of ash generated at Secunda Synfuels Operations are the Steam plant and Gasification plant where synthesis gas and steam are generated respectively.
Ash from the gasification process is made up of an 80 % coarse ash fraction, which is transported to the coarse ash heaps via conveyor belts, and a 20 % fine ash fraction which is transported to the fine ash dams in a slurry form by means of pumping.
Ash from the combustion process is made up of 86.4 % fine ash, which is transported to the fine ash dams together with the gasification fine ash fraction. The remaining 13.6% coarse ash is transported to the ash heaps together with the gasification coarse ash fraction.
PRODUCTION PROCESS FLOW CHART ATTACHED
YES X NO
IDENTIFICATION OF HAZARDS
WASTE CLASSIFICATION
HAZARDOUS GENERAL
X IF WASTE IS HAZARDOUS LIST THE HAZARDS OF THE WASTE
Health hazards due to the presence of lime (CaO) and SiO2 occurring as quartz
*A process flow chart must be attached to the process description
Page 3 of 7
RISK ASSESSEMENT WITHOUT MITIGATION
Activity Risk Description
Environmental receptors
Impact Assessment of the risk
Probability Magnitude
Duration Scale Significance
1. Loading of ash onto trucks
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
2. Transportation of ash
Loss of containment of ash
Air Dust generation along
transportation route Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Local: 2
Inherent: 25, low environmental significance
Land Load of ash deposited on
land in the vicinity of the road Land pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Load of ash deposited in
water body in the vicinity of the road
Water pollution
Inherent: Medium probability: 3
Inherent: Moderate: 6
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 27, low environmental significance
3. Off-loading of ash Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
4. Storage of ash Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Highly probable: 4
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 16, low environmental significance
Land Ash carried by run-off
deposited on land in the vicinity of the ash storage area
Land degradation
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Water Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
5. Handling of ash (i.e. screening, crushing, blending etc.)
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor:2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
Page 4 of 7
Activity Risk Description
Environmental receptors
Impact Assessment of the risk
Probability Magnitude
Duration Scale Significance
6. Incorporation of coal ash in construction land applications
a. Road construction;
b. Foundations; c. Backfill in mine
workings; d. Landfill capping;
Improper incorporation of ash in construction land applications
Air Localised dust generation Air pollution
Inherent: Highly probable: 4
Inherent: Minor: 2
Inherent: Medium term (12 months to 5 years): 3
Inherent: Site only: 1
Inherent: 24, low environmental significance
Land Land degradation Inherent:
Low probability: 2
Inherent: Low: 4
Inherent: Long term (5 to 10 years): 4
Inherent: Site only: 1
Inherent: 18, low environmental significance
Water Ash carried by run-off and
deposited into surface and ground water sources (increase in Total Suspended Solids TSS)
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Medium term (12 months to 5 years): 3
Inherent: Site only: 1
Inherent: 18, low environmental significance
7. Disposal of ash and ash containing mixtures
Loss of containment of ash
Air Localised dust generation Air pollution
Residual: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Land Load of ash disposed illegally
on land Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Illegally disposed ash
reaching water body in the vicinity of the dumping area
Water pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
8. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 12, low environmental significance
Land Ash carried by run-off
deposited on land in the vicinity of the ash storage area
Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Ash carried by run-off
deposited in storm water channels and water body in
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Residual: Local: 2
Inherent:
Page 5 of 7
Activity Risk Description
Environmental receptors
Impact Assessment of the risk
Probability Magnitude
Duration Scale Significance
the vicinity of the ash storage area
Short term (0 to 12 months): 2
16, low environmental significance
Page 6 of 7
The following factors and criteria must be used to assess the impacts of the activities:
Criteria MAGNITUDE (Severity) DURATION
10 - Very high 5 – Permanent (longer than 10 years) 8 – High 4 - Long-term (5 to 10 years) 6 – Moderate 3 - Medium-term (12 months to 5 years) 4 – Low 2 - Short-term (0 to 12 months) 2 – Minor 1 – Immediate
SCALE PROBABILITY (Likelihood) 5 – International 5 - Definite 4 – National 4 - Highly probable 3 – Regional 3 - Medium probability 2 – Local 2 - Low probability 1 - Site only 1 – Improbable 0 – None 0 – None
Magnitude Magnitude measures the size of the impact
Duration Duration refers to the lifetime of the impact i.e. how long it will last
Scale The scale refers to the extent of the impact.
Probability The probability refers to the chance of impact to occur. The potential impact could be most likely to occur, unlikely, etc. Assessment of Significance of impact Significance rating of the potential impacts illustrates the importance of the impact itself. The size of area affected by pollution may be extremely high but the significance of this effect is dependent on the concentration or level of pollution in that area. In order to determine the significance of impact, the following method was used: Significance Points (SP) = (Magnitude + Duration + Scale) x Probability The values of SP are then ranged as follows:
Rating Description
SP >60 Indicates high environmental significance
An impact which could influence the decision about whether or not to proceed with the activities regardless of any possible mitigation.
SP 30 – 60 Indicates moderate environmental significance
An impact or benefit which is sufficiently important to require management and which could have an influence on the decision unless it is mitigated.
SP <30 Indicates low environmental significance
Impacts with little real effect and which will not have an influence on or require modification of the activities.
+ Positive impact An impact that is likely to result in positive consequences/effects
Page 7 of 7
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not Authorised( provide reasons)
Reference Number
Page 1 of 7
RISK ASSESSMENT IN TERMS OF REGULATION 8 OF THE WASTE EXCLUSION REGULATIONS
APPLICANT Sasol South Africa (Ltd)
WASTE STREAM OR PORTION OF A WASTE STREAM
Weathered coarse ash
BENEFICIAL USE/S
Sasol Weathered coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Inorganic fertilizer; (b) Soil ameliorant and conditioner; and (c) Bulking agent for composting.
WASTE GENERATING FACILITY OR FACILITIES
PHYSICAL ADDRESS OF FACILITY OR FACILITIES
PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY OR FACILITIES
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
CONTACT PERSON
NAME Kashmira Doelab (Secunda Synfuels Operations (SSO): Acting Manager SHE: Waste)
ADDRESS Private Bag X1000 Secunda
2302
EMAIL ADDRESS [email protected]
TELEPHONE
+27 17 610 7143
+27 72 580 9842
Page 2 of 7
* DETAILED DESCRIPTION OF WASTE GENERATING PROCESS
Secunda Synfuels Operations Process: The sources of ash generated at Secunda Synfuels Operations are the Steam plant and Gasification plant where synthesis gas and steam are generated respectively.
Ash from the gasification process is made up of an 80 % coarse ash fraction, which is transported to the coarse ash heaps via conveyor belts, and a 20 % fine ash fraction which is transported to the fine ash dams in a slurry form by means of pumping.
Ash from the combustion process is made up of 86.4 % fine ash, which is transported to the fine ash dams together with the gasification fine ash fraction. The remaining 13.6% coarse ash is transported to the ash heaps together with the gasification coarse ash fraction.
PRODUCTION PROCESS FLOW CHART ATTACHED
YES X NO
IDENTIFICATION OF HAZARDS
WASTE CLASSIFICATION
HAZARDOUS GENERAL
X IF WASTE IS HAZARDOUS LIST THE HAZARDS OF THE WASTE
Health hazards due to the presence of lime (CaO) and SiO2 occurring as quartz
*A process flow chart must be attached to the process description
Page 3 of 7
RISK ASSESSEMENT WITHOUT MITIGATION
Activity Risk Description
Environmental receptors
Impact Assessment of the risk
Probability Magnitude
Duration Scale Significance
1. Loading of ash onto trucks
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
2. Transportation of ash
Loss of containment of ash
Air Dust generation along
transportation route Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Local: 2
Inherent: 25, low environmental significance
Land Load of ash deposited on
land in the vicinity of the road Land pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Load of ash deposited in
water body in the vicinity of the road
Water pollution
Inherent: Medium probability: 3
Inherent: Moderate: 6
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 27, low environmental significance
3. Off-loading of ash Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
4. Storage of ash Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Highly probable: 4
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 16, low environmental significance
Land Ash carried by run-off
deposited on land in the vicinity of the ash storage area
Land degradation
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Water Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
5. Handling of ash (i.e. screening, crushing, blending etc.)
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Definite: 5
Inherent: Minor:2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
Page 4 of 7
Activity Risk Description
Environmental receptors
Impact Assessment of the risk
Probability Magnitude
Duration Scale Significance
6. Incorporation of coal ash in agricultural land applications a. Inorganic
fertilizer; b. Soil ameliorant
and conditioner; and
c. Bulking agent for composting.
Improper incorporation of ash in agricultural land applications
Air Localised dust generation Air pollution
Inherent: Highly probable: 4
Inherent: Minor: 2
Inherent: Medium term (12 months to 5 years): 3
Inherent: Site only: 1
Inherent: 24, low environmental significance
Land Land degradation Inherent:
Low probability: 2
Inherent: Low: 4
Inherent: Long term (5 to 10 years): 4
Inherent: Site only: 1
Inherent: 18, low environmental significance
Water Ash carried by run-off and
deposited into surface and ground water sources (increase in Total Suspended Solids TSS)
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Medium term (12 months to 5 years): 3
Inherent: Site only: 1
Inherent: 18, low environmental significance
7. Disposal of ash and ash containing mixtures
Loss of containment of ash
Air Localised dust generation Air pollution
Residual: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Land Load of ash disposed illegally
on land Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Illegally disposed ash
reaching water body in the vicinity of the dumping area
Water pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
8. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Air Localised dust generation Air pollution
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 12, low environmental significance
Land Ash carried by run-off
deposited on land in the vicinity of the ash storage area
Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water Ash carried by run-off
deposited in storm water channels and water body in
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Residual: Local: 2
Inherent:
Page 5 of 7
Activity Risk Description
Environmental receptors
Impact Assessment of the risk
Probability Magnitude
Duration Scale Significance
the vicinity of the ash storage area
Short term (0 to 12 months): 2
16, low environmental significance
Page 6 of 7
The following factors and criteria must be used to assess the impacts of the activities:
Criteria MAGNITUDE (Severity) DURATION
10 - Very high 5 – Permanent (longer than 10 years) 8 – High 4 - Long-term (5 to 10 years) 6 – Moderate 3 - Medium-term (12 months to 5 years) 4 – Low 2 - Short-term (0 to 12 months) 2 – Minor 1 – Immediate
SCALE PROBABILITY (Likelihood) 5 – International 5 - Definite 4 – National 4 - Highly probable 3 – Regional 3 - Medium probability 2 – Local 2 - Low probability 1 - Site only 1 – Improbable 0 – None 0 – None
Magnitude Magnitude measures the size of the impact
Duration Duration refers to the lifetime of the impact i.e. how long it will last
Scale The scale refers to the extent of the impact.
Probability The probability refers to the chance of impact to occur. The potential impact could be most likely to occur, unlikely, etc. Assessment of Significance of impact Significance rating of the potential impacts illustrates the importance of the impact itself. The size of area affected by pollution may be extremely high but the significance of this effect is dependent on the concentration or level of pollution in that area. In order to determine the significance of impact, the following method was used: Significance Points (SP) = (Magnitude + Duration + Scale) x Probability The values of SP are then ranged as follows:
Rating Description
SP >60 Indicates high environmental significance
An impact which could influence the decision about whether or not to proceed with the activities regardless of any possible mitigation.
SP 30 – 60 Indicates moderate environmental significance
An impact or benefit which is sufficiently important to require management and which could have an influence on the decision unless it is mitigated.
SP <30 Indicates low environmental significance
Impacts with little real effect and which will not have an influence on or require modification of the activities.
+ Positive impact An impact that is likely to result in positive consequences/effects
Page 7 of 7
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not Authorised( provide reasons)
Reference Number
Page 1 of 6
RISK ASSESSMENT IN TERMS OF REGULATION 8 OF THE WASTE EXCLUSION REGULATIONS
APPLICANT Sasol South Africa (Ltd)
WASTE STREAM OR PORTION OF A WASTE STREAM
Weathered coarse ash
BENEFICIAL USE/S
Sasol Weathered coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Aggregate
WASTE GENERATING FACILITY OR FACILITIES
PHYSICAL ADDRESS OF FACILITY OR FACILITIES
PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY OR FACILITIES
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
CONTACT PERSON
NAME Kashmira Doelab (Secunda Synfuels Operations (SSO): Acting Manager SHE: Waste)
ADDRESS Private Bag X1000 Secunda 2302
EMAIL ADDRESS [email protected]
TELEPHONE
+27 17 610 7143 +27 72 580 9842
Page 2 of 6
* DETAILED DESCRIPTION OF WASTE GENERATING PROCESS
Secunda Synfuels Operations Process: The sources of ash generated at Secunda Synfuels Operations are the Steam plant and Gasification plant where synthesis gas and steam are generated respectively.
Ash from the gasification process is made up of an 80 % coarse ash fraction, which is transported to the coarse ash heaps via conveyor belts, and a 20 % fine ash fraction which is transported to the fine ash dams in a slurry form by means of pumping.
Ash from the combustion process is made up of 86.4 % fine ash, which is transported to the fine ash dams together with the gasification fine ash fraction. The remaining 13.6% coarse ash is transported to the ash heaps together with the gasification coarse ash fraction.
PRODUCTION PROCESS FLOW CHART ATTACHED
YES X NO
IDENTIFICATION OF HAZARDS
WASTE CLASSIFICATION
HAZARDOUS GENERAL
X IF WASTE IS HAZARDOUS LIST THE HAZARDS OF THE WASTE
Health hazards due to the presence of lime (CaO) and SiO2 occurring as quartz
*A process flow chart must be attached to the process description
Page 3 of 6
RISK ASSESSEMENT WITHOUT MITIGATION
Activity Risk Description
Environmental receptors
Impact Assessment of the risk Significance
Probability Magnitude
Duration Scale
1. Loading of ash onto trucks
Loss of containment of ash
Air • Localised dust generation • Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
2. Transportation of ash
Loss of containment of ash
Air • Dust generation along
transportation route • Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Local: 2
Inherent: 25, low environmental significance
Land • Load of ash deposited on
land in the vicinity of the road • Land pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water • Load of ash deposited in
water body in the vicinity of the road
• Water pollution
Inherent: Medium probability: 3
Inherent: Moderate: 6
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 27, low environmental significance
3. Off-loading of ash Loss of containment of ash
Air • Localised dust generation • Air pollution
Inherent: Definite: 5
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
4. Storage of ash Loss of containment of ash
Air • Localised dust generation • Air pollution
Inherent: Highly probable: 4
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 16, low environmental significance
Land • Ash carried by run-off
deposited on land in the vicinity of the ash storage area
• Land degradation
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Water • Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
5. Handling of ash which includes the production of
Loss of containment of ash
Air • Localised dust generation • Air pollution
Inherent: Definite: 5
Inherent: Minor:2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 20, low environmental significance
Page 4 of 6
aggregate (i.e. screening, crushing, blending etc.)
6. Disposal of ash and ash containing products
Loss of containment of ash
Air • Localised dust generation • Air pollution
Residual: Medium probability: 3
Inherent: Minor: 2
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 15, low environmental significance
Land • Load of ash disposed illegally
on land • Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water • Illegally disposed ash
reaching water body in the vicinity of the dumping area
• Water pollution
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
7. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Air • Localised dust generation • Air pollution
Inherent: Medium probability: 3
Inherent: Minor: 2
Inherent: Immediate: 1
Inherent: Site only: 1
Inherent: 12, low environmental significance
Land • Ash carried by run-off
deposited on land in the vicinity of the ash storage area
• Land degradation
Inherent: Medium probability: 3
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Inherent: Site only: 1
Inherent: 21, low environmental significance
Water • Ash carried by run-off
deposited in storm water channels and water body in the vicinity of the ash storage area
Inherent: Low probability: 2
Inherent: Low: 4
Inherent: Short term (0 to 12 months): 2
Residual: Local: 2
Inherent: 16, low environmental significance
Page 5 of 6
The following factors and criteria must be used to assess the impacts of the activities:
Criteria MAGNITUDE (Severity) DURATION
10 - Very high 5 – Permanent (longer than 10 years) 8 – High 4 - Long-term (5 to 10 years) 6 – Moderate 3 - Medium-term (12 months to 5 years) 4 – Low 2 - Short-term (0 to 12 months) 2 – Minor 1 – Immediate
SCALE PROBABILITY (Likelihood) 5 – International 5 - Definite 4 – National 4 - Highly probable 3 – Regional 3 - Medium probability 2 – Local 2 - Low probability 1 - Site only 1 – Improbable 0 – None 0 – None
Magnitude Magnitude measures the size of the impact
Duration Duration refers to the lifetime of the impact i.e. how long it will last
Scale The scale refers to the extent of the impact.
Probability The probability refers to the chance of impact to occur. The potential impact could be most likely to occur, unlikely, etc. Assessment of Significance of impact Significance rating of the potential impacts illustrates the importance of the impact itself. The size of area affected by pollution may be extremely high but the significance of this effect is dependent on the concentration or level of pollution in that area. In order to determine the significance of impact, the following method was used: Significance Points (SP) = (Magnitude + Duration + Scale) x Probability The values of SP are then ranged as follows:
Rating Description
SP >60 Indicates high environmental significance
An impact which could influence the decision about whether or not to proceed with the activities regardless of any possible mitigation.
SP 30 – 60 Indicates moderate environmental significance
An impact or benefit which is sufficiently important to require management and which could have an influence on the decision unless it is mitigated.
SP <30 Indicates low environmental significance
Impacts with little real effect and which will not have an influence on or require modification of the activities.
+ Positive impact An impact that is likely to result in positive consequences/effects
Page 6 of 6
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not Authorised( provide reasons)
Reference Number
Page 1 of 4
RISK MANAGEMENT PLAN IN TERMS OF REGULATION 10 OF WASTE EXCLUSION REGULATONS
APPLICANT
Sasol South Africa (Ltd)
SOURCE(S) OF WASTE
Secunda Synfuels Operations (gasifiers)
WASTE TO BE BENEFICIATED
Fresh coarse ash
BENEFICIAL USE/S Sasol Fresh coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Brickmaking; (b) Block making; (c) Production of cement.
SDS ATTACHED IF HAZARDOUS
YES X NO
WASTE GENERATING FACILITY
Secunda Synfuels Operations (gasifiers)
PHYSICAL ADDRESS PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY (e.g. 600 29′ 30″ Latitude; 34⁰ 20′ 15″ Longitude)
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
POSTAL ADDRESS Private Bag X1000 Secunda
2302
Page 2 of 4
CONTACT PERSON Kashmira Doelab (Secunda Synfuels Operations (SSO): Acting Manager SHE: Waste)
TELEPHONE +27 17 610 7143 CELL: 072 580 9842
EMAIL [email protected] FAX: None
RISK MANAGEMENT PLAN
Activity Risk Description
Action(s) to minimise/ manage the risk Responsibility (Who is responsible to do it)
1. Loading of ash onto trucks
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Stop loading of ash during extreme wind conditions
Ash generator i.e. Sasolburg Operations and Secunda Operations
Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash loading
Ash generator employees Ash transporter employees
2. Transportation of ash
Loss of containment of ash
Preventative mitigation measure Dust management during transportation will include
ensuring vehicles follow an approved route that will limit the exposure of dust in communities.
Side tippers with tarpaulin devices will be recommended for the transportation of ash, however, those that cannot be covered will not be filled to capacity and will be required to go through a dust suppression (wetting) process.
Corrective mitigation measure None
Ash transporters
Preventative mitigation measure Compliance with the Road Traffic Act; Sasol Transport Policy and Procedures; Access to ash limited to customers and transporters
that have commercial contracts with Sasol. Corrective mitigation measure Implementation of the Emergency response plan; Use of Safety Data Sheet (SDS) with hazard
classification which is provided to all customers and transporters.
3. Off-loading of ash
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Stop off-loading of ash during extreme wind
conditions Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash off-loading
Ash transporters Ash users
4. Storage of ash Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Avoid loading of ash during extreme wind conditions Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) when working in ash storage area
Ash users
Page 3 of 4
Activity Risk Description
Action(s) to minimise/ manage the risk Responsibility (Who is responsible to do it)
Preventative mitigation measure Storage area designed to prevent rainfall run-off from
carrying ash away Discourage excessive storage of ash - Facilities
storing more than a 100 m3 of ash at a time, should have a firm impermeable surface on which to place the ash and a system to collect and store run-off arising from the ash storage facility.
Corrective mitigation measure The use of Safety Data Sheet (SDS) with hazard
classification which is provided to all ash users. Clean-up plan to be implemented where ash is
carried way from storage area 5. Handling of ash
(i.e. screening, crushing, blending etc.)
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Adherence to production process and product
standards and regulations
Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash handling
Ash users
a. Brickmaking; b. Block
making; c. Production of
cement.
The point at which coal ash enters the production process of bricks, blocks and cement to the actual products is outside the scope of this risk assessment. The incorporation of coal ash into these existing production processes is matured. The quality of the products from these processes is regulated by relevant standards.
Ash users
6. Disposal of ash and ash containing products
Loss of containment of ash
Preventative mitigation measure The use of Safety Data Sheet (SDS) where disposal
guidance is provided. The use of the National Norms and standard for the
assessment of waste for disposal and the Regulations for the classification and management of waste.
Corrective mitigation measure Clean-up plan to be implemented where ash is not
disposed properly.
Ash users
7. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Preventative mitigation measure Contractual agreement with ash customers to include
the following clause: "The owner of the facility, including the subsequent owner of the facility will remain responsible for any adverse impacts on the environment and health stemming from stockpiled ash, even after operations have ceased."
Corrective mitigation measure Land remediation
Ash users
Page 4 of 4
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not authorised (provide reason)
Reference Number
Page 1 of 4
RISK MANAGEMENT PLAN IN TERMS OF REGULATION 10 OF WASTE EXCLUSION REGULATONS
APPLICANT
Sasol South Africa (Ltd)
SOURCE(S) OF WASTE
Secunda Synfuels Operations (gasifiers)
WASTE TO BE BENEFICIATED
Fresh coarse ash
BENEFICIAL USE/S Sasol Fresh coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Road construction; (b) Foundations; (c) Backfill in mine workings; (d) Landfill capping.
SDS ATTACHED IF HAZARDOUS
YES X NO
WASTE GENERATING FACILITY
Secunda Synfuels Operations (gasifiers)
PHYSICAL ADDRESS PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY (e.g. 600 29′ 30″ Latitude; 34⁰ 20′ 15″ Longitude)
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
POSTAL ADDRESS Private Bag X1000 Secunda
2302
Page 2 of 4
CONTACT PERSON Kashmira Doelab (Secunda Synfuels Operations (SSO): Manager SHE: Waste)
TELEPHONE +27 17 610 7143 CELL: 072 580 9842
EMAIL [email protected] FAX: None
RISK MANAGEMENT PLAN
Activity Risk Description
Action(s) to minimise/ manage the risk Responsibility (Who is responsible to do it)
1. Loading of ash onto trucks
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Stop loading of ash during extreme wind conditions
Ash generator i.e. Sasolburg Operations and Secunda Operations
Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash loading
Ash generator employees Ash transporter employees
2. Transportation of ash
Loss of containment of ash
Preventative mitigation measure Dust management during transportation will include
ensuring vehicles follow an approved route that will limit the exposure of dust in communities.
Side tippers with tarpaulin devices will be recommended for the transportation of ash, however, those that cannot be covered will not be filled to capacity and will be required to go through a dust suppression (wetting) process.
Corrective mitigation measure None
Ash transporters
Preventative mitigation measure Compliance with the Road Traffic Act; Sasol Transport Policy and Procedures; Access to ash limited to customers and transporters
that have commercial contracts with Sasol. Corrective mitigation measure Implementation of the Emergency response plan; Use of Safety Data Sheet (SDS) with hazard
classification which is provided to all customers and transporters.
3. Off-loading of ash
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Stop off-loading of ash during extreme wind
conditions Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash off-loading
Ash transporters Ash users
4. Storage of ash Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Avoid loading of ash during extreme wind conditions Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) when working in ash storage area
Ash users
Preventative mitigation measure
Page 3 of 4
Activity Risk Description
Action(s) to minimise/ manage the risk Responsibility (Who is responsible to do it)
Storage area designed to prevent rainfall run-off from carrying ash away
Discourage excessive storage of ash - Facilities storing more than a 100 m3 of ash at a time, should have a firm impermeable surface on which to place the ash and a system to collect and store run-off arising from the ash storage facility.
Corrective mitigation measure The use of Safety Data Sheet (SDS) with hazard
classification which is provided to all ash users. Clean-up plan to be implemented where ash is
carried way from storage area 5. Handling of ash
(i.e. screening, crushing, blending etc.)
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Adherence to production process and product
standards and regulations
Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash handling
Ash users
6. Incorporation of coal ash in construction land applications
a. Road construction;
b. Foundations; c. Backfill in mine
workings; d. Landfill capping.
Improper incorporation of ash in construction land applications
Preventative mitigation measure Substitution of natural materials with ash must meet
sector standards for the various works
Corrective mitigation measure Land remediation
Ash users
7. Disposal of ash and ash containing products
Loss of containment of ash
Preventative mitigation measure The use of Safety Data Sheet (SDS) where disposal
guidance is provided. The use of the National Norms and standard for the
assessment of waste for disposal and the Regulations for the classification and management of waste.
Corrective mitigation measure Clean-up plan to be implemented where ash is not
disposed properly.
Ash users
8. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Preventative mitigation measure Contractual agreement with ash customers to include
the following clause: "The owner of the facility, including the subsequent owner of the facility will remain responsible for any adverse impacts on the environment and health stemming from stockpiled ash, even after operations have ceased."
Corrective mitigation measure Land remediation
Ash users
Page 4 of 4
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not authorised (provide reason)
Reference Number
Page 1 of 4
RISK MANAGEMENT PLAN IN TERMS OF REGULATION 10 OF WASTE EXCLUSION REGULATONS
APPLICANT
Sasol South Africa (Ltd)
SOURCE(S) OF WASTE
Secunda Synfuels Operations (gasifiers)
WASTE TO BE BENEFICIATED
Fresh coarse ash
BENEFICIAL USE/S Sasol Fresh coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Inorganic fertilizer; (b) Soil ameliorant and conditioner; (c) Bulking agent for composting.
SDS ATTACHED IF HAZARDOUS
YES X NO
WASTE GENERATING FACILITY
Secunda Synfuels Operations (gasifiers)
PHYSICAL ADDRESS PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY (e.g. 600 29′ 30″ Latitude; 34⁰ 20′ 15″ Longitude)
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
POSTAL ADDRESS Private Bag X1000 Secunda
2302
Page 2 of 4
CONTACT PERSON Kashmira Doelab (Secunda Synfuels Operations (SSO): Acting Manager SHE: Waste)
TELEPHONE +27 17 610 7143 CELL: 072 580 9842
EMAIL [email protected] FAX: None
RISK MANAGEMENT PLAN
Activity Risk Description
Action(s) to minimise/ manage the risk Responsibility (Who is responsible to do it)
1. Loading of ash onto trucks
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Stop loading of ash during extreme wind conditions
Ash generator i.e. Sasolburg Operations and Secunda Operations
Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash loading
Ash generator employees
Ash transporter employees
2. Transportation of ash
Loss of containment of ash
Preventative mitigation measure Dust management during transportation will include
ensuring vehicles follow an approved route that will limit the exposure of dust in communities.
Side tippers with tarpaulin devices will be recommended for the transportation of ash, however, those that cannot be covered will not be filled to capacity and will be required to go through a dust suppression (wetting) process.
Corrective mitigation measure None
Ash transporters
Preventative mitigation measure Compliance with the Road Traffic Act; Sasol Transport Policy and Procedures; Access to ash limited to customers and transporters
that have commercial contracts with Sasol. Corrective mitigation measure Implementation of the Emergency response plan; Use of Safety Data Sheet (SDS) with hazard
classification which is provided to all customers and transporters.
3. Off-loading of ash
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Stop off-loading of ash during extreme wind
conditions Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash off-loading
Ash transporters Ash users
4. Storage of ash Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Avoid loading of ash during extreme wind conditions Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) when working in ash storage area
Ash users
Preventative mitigation measure
Page 3 of 4
Activity Risk Description
Action(s) to minimise/ manage the risk Responsibility (Who is responsible to do it)
Storage area designed to prevent rainfall run-off from carrying ash away
Discourage excessive storage of ash - Facilities storing more than a 100 m3 of ash at a time, should have a firm impermeable surface on which to place the ash and a system to collect and store run-off arising from the ash storage facility.
Corrective mitigation measure The use of Safety Data Sheet (SDS) with hazard
classification which is provided to all ash users. Clean-up plan to be implemented where ash is
carried way from storage area 5. Handling of ash
(i.e. screening, crushing, blending etc.)
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Adherence to production process and product
standards and regulations
Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash handling
Ash users
6. Incorporation of coal ash in agricultural land applications
a. Inorganic fertilizer;
b. Soil ameliorant and conditioner;
c. Bulking agent for composting.
Improper incorporation of ash in agricultural land applications
Preventative mitigation measure Agricultural products including ash must meet
requirements from relevant regulations Application of ash containing products on agricultural
land to be done in a modular fashion, in accordance with agricultural norms and site specific requirements
Corrective mitigation measure Land remediation
Ash users
7. Disposal of ash and ash containing products
Loss of containment of ash
Preventative mitigation measure The use of Safety Data Sheet (SDS) where disposal
guidance is provided. The use of the National Norms and standard for the
assessment of waste for disposal and the Regulations for the classification and management of waste.
Corrective mitigation measure Clean-up plan to be implemented where ash is not
disposed properly.
Ash users
8. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Preventative mitigation measure Contractual agreement with ash customers to include
the following clause: "The owner of the facility, including the subsequent owner of the facility will remain responsible for any adverse impacts on the environment and health stemming from stockpiled ash, even after operations have ceased."
Corrective mitigation measure Land remediation
Ash users
Page 4 of 4
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not authorised (provide reason)
Reference Number
Page 1 of 4
RISK MANAGEMENT PLAN IN TERMS OF REGULATION 10 OF WASTE EXCLUSION REGULATONS
APPLICANT
Sasol South Africa (Ltd)
SOURCE(S) OF WASTE
Secunda Synfuels Operations (gasifiers)
WASTE TO BE BENEFICIATED
Weathered coarse ash
BENEFICIAL USE/S Sasol Weathered coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Brickmaking; (b) Block making; (c) Production of cement.
SDS ATTACHED IF HAZARDOUS
YES X NO
WASTE GENERATING FACILITY
Secunda Synfuels Operations (gasifiers)
PHYSICAL ADDRESS PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY (e.g. 600 29′ 30″ Latitude; 34⁰ 20′ 15″ Longitude)
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
POSTAL ADDRESS Private Bag X1000 Secunda
2302
Page 2 of 4
CONTACT PERSON Kashmira Doelab (Secunda Synfuels Operations (SSO): Acting Manager SHE: Waste)
TELEPHONE +27 17 610 7143 CELL: 072 580 9842
EMAIL [email protected] FAX: None
RISK MANAGEMENT PLAN
Activity Risk Description
Action(s) to minimise/ manage the risk Responsibility (Who is responsible to do it)
1. Loading of ash onto trucks
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Stop loading of ash during extreme wind conditions
Ash generator i.e. Sasolburg Operations and Secunda Operations
Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash loading
Ash generator employees Ash transporter employees
2. Transportation of ash
Loss of containment of ash
Preventative mitigation measure Dust management during transportation will include
ensuring vehicles follow an approved route that will limit the exposure of dust in communities.
Side tippers with tarpaulin devices will be recommended for the transportation of ash, however, those that cannot be covered will not be filled to capacity and will be required to go through a dust suppression (wetting) process.
Corrective mitigation measure None
Ash transporters
Preventative mitigation measure Compliance with the Road Traffic Act; Sasol Transport Policy and Procedures; Access to ash limited to customers and transporters
that have commercial contracts with Sasol. Corrective mitigation measure Implementation of the Emergency response plan; Use of Safety Data Sheet (SDS) with hazard
classification which is provided to all customers and transporters.
3. Off-loading of ash
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Stop off-loading of ash during extreme wind
conditions Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash off-loading
Ash transporters Ash users
4. Storage of ash Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Avoid loading of ash during extreme wind conditions Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) when working in ash storage area
Ash users
Page 3 of 4
Activity Risk Description
Action(s) to minimise/ manage the risk Responsibility (Who is responsible to do it)
Preventative mitigation measure Storage area designed to prevent rainfall run-off from
carrying ash away Discourage excessive storage of ash - Facilities
storing more than a 100 m3 of ash at a time, should have a firm impermeable surface on which to place the ash and a system to collect and store run-off arising from the ash storage facility.
Corrective mitigation measure The use of Safety Data Sheet (SDS) with hazard
classification which is provided to all ash users. Clean-up plan to be implemented where ash is
carried way from storage area 5. Handling of ash
(i.e. screening, crushing, blending etc.)
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Adherence to production process and product
standards and regulations
Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash handling
Ash users
a. Brickmaking; b. Block
making; c. Production of
cement.
The point at which coal ash enters the production process of bricks, blocks and cement to the actual products is outside the scope of this risk assessment. The incorporation of coal ash into these existing production processes is matured. The quality of the products from these processes is regulated by relevant standards.
Ash users
6. Disposal of ash and ash containing products
Loss of containment of ash
Preventative mitigation measure The use of Safety Data Sheet (SDS) where disposal
guidance is provided. The use of the National Norms and standard for the
assessment of waste for disposal and the Regulations for the classification and management of waste.
Corrective mitigation measure Clean-up plan to be implemented where ash is not
disposed properly.
Ash users
7. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Preventative mitigation measure Contractual agreement with ash customers to include
the following clause: "The owner of the facility, including the subsequent owner of the facility will remain responsible for any adverse impacts on the environment and health stemming from stockpiled ash, even after operations have ceased."
Corrective mitigation measure Land remediation
Ash users
Page 4 of 4
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not authorised (provide reason)
Reference Number
Page 1 of 4
RISK MANAGEMENT PLAN IN TERMS OF REGULATION 10 OF WASTE EXCLUSION REGULATONS
APPLICANT
Sasol South Africa (Ltd)
SOURCE(S) OF WASTE
Secunda Synfuels Operations (gasifiers)
WASTE TO BE BENEFICIATED
Weathered coarse ash
BENEFICIAL USE/S Sasol Weathered coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Road construction; (b) Foundations; (c) Backfill in mine workings; (d) Landfill capping.
SDS ATTACHED IF HAZARDOUS
YES X NO
WASTE GENERATING FACILITY
Secunda Synfuels Operations (gasifiers)
PHYSICAL ADDRESS PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY (e.g. 600 29′ 30″ Latitude; 34⁰ 20′ 15″ Longitude)
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
POSTAL ADDRESS Private Bag X1000 Secunda
2302
Page 2 of 4
CONTACT PERSON Kashmira Doelab (Secunda Synfuels Operations (SSO): Acting Manager SHE: Waste)
TELEPHONE +27 17 610 7143 CELL: 072 580 9842
EMAIL [email protected] FAX: None
RISK MANAGEMENT PLAN
Activity Risk Description
Action(s) to minimise/ manage the risk Responsibility (Who is responsible to do it)
1. Loading of ash onto trucks
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Stop loading of ash during extreme wind conditions
Ash generator i.e. Sasolburg Operations and Secunda Operations
Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash loading
Ash generator employees Ash transporter employees
2. Transportation of ash
Loss of containment of ash
Preventative mitigation measure Dust management during transportation will include
ensuring vehicles follow an approved route that will limit the exposure of dust in communities.
Side tippers with tarpaulin devices will be recommended for the transportation of ash, however, those that cannot be covered will not be filled to capacity and will be required to go through a dust suppression (wetting) process.
Corrective mitigation measure None
Ash transporters
Preventative mitigation measure Compliance with the Road Traffic Act; Sasol Transport Policy and Procedures; Access to ash limited to customers and transporters
that have commercial contracts with Sasol. Corrective mitigation measure Implementation of the Emergency response plan; Use of Safety Data Sheet (SDS) with hazard
classification which is provided to all customers and transporters.
3. Off-loading of ash
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Stop off-loading of ash during extreme wind
conditions Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash off-loading
Ash transporters Ash users
4. Storage of ash Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Avoid loading of ash during extreme wind conditions Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) when working in ash storage area
Ash users
Page 3 of 4
Activity Risk Description
Action(s) to minimise/ manage the risk Responsibility (Who is responsible to do it)
Preventative mitigation measure Storage area designed to prevent rainfall run-off from
carrying ash away Discourage excessive storage of ash - Facilities
storing more than a 100 m3 of ash at a time, should have a firm impermeable surface on which to place the ash and a system to collect and store run-off arising from the ash storage facility.
Corrective mitigation measure The use of Safety Data Sheet (SDS) with hazard
classification which is provided to all ash users. Clean-up plan to be implemented where ash is
carried way from storage area 5. Handling of ash
(i.e. screening, crushing, blending etc.)
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Adherence to production process and product
standards and regulations
Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash handling
Ash users
6. Incorporation of coal ash in construction land applications
a. Road construction;
b. Foundations; c. Backfill in mine
workings; d. Landfill capping.
Improper incorporation of ash in construction land applications
Preventative mitigation measure Substitution of natural materials with ash must meet
sector standards for the various works
Corrective mitigation measure Land remediation
Ash users
7. Disposal of ash and ash containing products
Loss of containment of ash
Preventative mitigation measure The use of Safety Data Sheet (SDS) where disposal
guidance is provided. The use of the National Norms and standard for the
assessment of waste for disposal and the Regulations for the classification and management of waste.
Corrective mitigation measure Clean-up plan to be implemented where ash is not
disposed properly.
Ash users
8. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Preventative mitigation measure Contractual agreement with ash customers to include
the following clause: "The owner of the facility, including the subsequent owner of the facility will remain responsible for any adverse impacts on the environment and health stemming from stockpiled ash, even after operations have ceased."
Corrective mitigation measure Land remediation
Ash users
Page 4 of 4
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not authorised (provide reason)
Reference Number
Page 1 of 4
RISK MANAGEMENT PLAN IN TERMS OF REGULATION 10 OF WASTE EXCLUSION REGULATONS
APPLICANT
Sasol South Africa (Ltd)
SOURCE(S) OF WASTE
Secunda Synfuels Operations (gasifiers)
WASTE TO BE BENEFICIATED
Weathered coarse ash
BENEFICIAL USE/S Sasol Weathered coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Inorganic fertilizer; (b) Soil ameliorant and conditioner; (c) Bulking agent for composting.
SDS ATTACHED IF HAZARDOUS
YES X NO
WASTE GENERATING FACILITY
Secunda Synfuels Operations (gasifiers)
PHYSICAL ADDRESS PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY (e.g. 600 29′ 30″ Latitude; 34⁰ 20′ 15″ Longitude)
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
POSTAL ADDRESS Private Bag X1000 Secunda
2302
Page 2 of 4
CONTACT PERSON Kashmira Doelab (Secunda Synfuels Operations (SSO): Acting Manager SHE: Waste)
TELEPHONE +27 17 610 7143 CELL: 072 580 9842
EMAIL [email protected] FAX: None
RISK MANAGEMENT PLAN
Activity Risk Description
Action(s) to minimise/ manage the risk Responsibility (Who is responsible to do it)
1. Loading of ash onto trucks
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Stop loading of ash during extreme wind conditions
Ash generator i.e. Sasolburg Operations and Secunda Operations
Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash loading
Ash generator employees Ash transporter employees
2. Transportation of ash
Loss of containment of ash
Preventative mitigation measure Dust management during transportation will include
ensuring vehicles follow an approved route that will limit the exposure of dust in communities.
Side tippers with tarpaulin devices will be recommended for the transportation of ash, however, those that cannot be covered will not be filled to capacity and will be required to go through a dust suppression (wetting) process.
Corrective mitigation measure None
Ash transporters
Preventative mitigation measure Compliance with the Road Traffic Act; Sasol Transport Policy and Procedures; Access to ash limited to customers and transporters
that have commercial contracts with Sasol. Corrective mitigation measure Implementation of the Emergency response plan; Use of Safety Data Sheet (SDS) with hazard
classification which is provided to all customers and transporters.
3. Off-loading of ash
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Stop off-loading of ash during extreme wind
conditions Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash off-loading
Ash transporters Ash users
4. Storage of ash Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Avoid loading of ash during extreme wind conditions Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) when working in ash storage area
Ash users
Page 3 of 4
Activity Risk Description
Action(s) to minimise/ manage the risk Responsibility (Who is responsible to do it)
Preventative mitigation measure Storage area designed to prevent rainfall run-off from
carrying ash away Discourage excessive storage of ash - Facilities
storing more than a 100 m3 of ash at a time, should have a firm impermeable surface on which to place the ash and a system to collect and store run-off arising from the ash storage facility.
Corrective mitigation measure The use of Safety Data Sheet (SDS) with hazard
classification which is provided to all ash users. Clean-up plan to be implemented where ash is
carried way from storage area 5. Handling of ash
(i.e. screening, crushing, blending etc.)
Loss of containment of ash
Preventative mitigation measure Dust management during loading of ash through
wetting of ash Adherence to production process and product
standards and regulations
Corrective mitigation measure Wearing of relevant PPE (dust mask and eye
protection) during ash handling
Ash users
6. Incorporation of coal ash in agricultural land applications
a. Inorganic fertilizer;
b. Soil ameliorant and conditioner;
c. Bulking agent for composting.
Improper incorporation of ash in agricultural land applications
Preventative mitigation measure Agricultural products including ash must meet
requirements from relevant regulations Application of ash containing products on agricultural
land to be done in a modular fashion, in accordance with agricultural norms and site specific requirements
Corrective mitigation measure Land remediation
Ash users
7. Disposal of ash and ash containing products
Loss of containment of ash
Preventative mitigation measure The use of Safety Data Sheet (SDS) where disposal
guidance is provided. The use of the National Norms and standard for the
assessment of waste for disposal and the Regulations for the classification and management of waste.
Corrective mitigation measure Clean-up plan to be implemented where ash is not
disposed properly.
Ash users
8. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Preventative mitigation measure Contractual agreement with ash customers to include
the following clause: "The owner of the facility, including the subsequent owner of the facility will remain responsible for any adverse impacts on the environment and health stemming from stockpiled ash, even after operations have ceased."
Corrective mitigation measure Land remediation
Ash users
Page 4 of 4
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not authorised (provide reason)
Reference Number
Page 1 of 4
RISK MANAGEMENT PLAN IN TERMS OF REGULATION 10 OF WASTE EXCLUSION REGULATONS
APPLICANT
Sasol South Africa (Ltd)
SOURCE(S) OF WASTE
Secunda Synfuels Operations (gasifiers)
WASTE TO BE BENEFICIATED
Weathered coarse ash
BENEFICIAL USE/S Sasol Weathered coarse ash may be beneficially utilised in the construction and agricultural sectors. Its uses may include but are not limited to:
(a) Aggregate
SDS ATTACHED IF HAZARDOUS
YES X NO
WASTE GENERATING FACILITY
Secunda Synfuels Operations (gasifiers)
PHYSICAL ADDRESS PdP Kruger Road, Secunda, 2302
GPS CO-ORDINATES OF WASTE GENERATING FACILITY (e.g. 600 29′ 30″ Latitude; 34⁰ 20′ 15″ Longitude)
260 32′ 23″ Latitude; 29⁰ 8′ 55″ Longitude 260 33′ 39″ Latitude; 29⁰ 8′ 41″ Longitude 260 33′ 56″ Latitude; 29⁰ 10′ 44″ Longitude 260 32′ 43″ Latitude; 29⁰ 10′ 55″ Longitude
POSTAL ADDRESS Private Bag X1000 Secunda 2302
CONTACT PERSON Kashmira Doelab (Secunda Synfuels Operations (SSO): Acting Manager SHE: Waste)
Page 2 of 4
TELEPHONE +27 17 610 7143 CELL: 072 580 9842
EMAIL [email protected] FAX: None
RISK MANAGEMENT PLAN Activity Risk
Description Action(s) to minimise/ manage the risk Responsibility
(Who is responsible to do it)
1. Loading of ash onto trucks
Loss of containment of ash
Preventative mitigation measure • Dust management during loading of ash through
wetting of ash • Stop loading of ash during extreme wind conditions
Ash generator i.e. Sasolburg Operations and Secunda Operations
Corrective mitigation measure • Wearing of relevant PPE (dust mask and eye
protection) during ash loading
Ash generator employees Ash transporter employees
2. Transportation of ash
Loss of containment of ash
Preventative mitigation measure • Dust management during transportation will include
ensuring vehicles follow an approved route that will limit the exposure of dust in communities.
• Side tippers with tarpaulin devices will be recommended for the transportation of ash, however, those that cannot be covered will not be filled to capacity and will be required to go through a dust suppression (wetting) process.
Corrective mitigation measure • None
Ash transporters
Preventative mitigation measure • Compliance with the Road Traffic Act; • Sasol Transport Policy and Procedures; • Access to ash limited to customers and transporters
that have commercial contracts with Sasol. Corrective mitigation measure • Implementation of the Emergency response plan; • Use of Safety Data Sheet (SDS) with hazard
classification which is provided to all customers and transporters.
3. Off-loading of ash
Loss of containment of ash
Preventative mitigation measure • Dust management during loading of ash through
wetting of ash • Stop off-loading of ash during extreme wind
conditions Corrective mitigation measure • Wearing of relevant PPE (dust mask and eye
protection) during ash off-loading
Ash transporters Ash users
4. Storage of ash Loss of containment of ash
Preventative mitigation measure • Dust management during loading of ash through
wetting of ash • Avoid loading of ash during extreme wind conditions Corrective mitigation measure • Wearing of relevant PPE (dust mask and eye
protection) when working in ash storage area
Ash users
Preventative mitigation measure • Storage area designed to prevent rainfall run-off from
carrying ash away
Page 3 of 4
Activity Risk Description
Action(s) to minimise/ manage the risk Responsibility (Who is responsible to do it)
• Discourage excessive storage of ash - Facilities storing more than a 100 m3 of ash at a time, should have a firm impermeable surface on which to place the ash and a system to collect and store run-off arising from the ash storage facility.
Corrective mitigation measure • The use of Safety Data Sheet (SDS) with hazard
classification which is provided to all ash users. • Clean-up plan to be implemented where ash is
carried way from storage area 5. Handling of ash
which includes the production of aggregate (i.e. screening, crushing, blending etc.)
Loss of containment of ash
Preventative mitigation measure • Dust management during loading of ash through
wetting of ash • Adherence to production process and product
standards and regulations
Corrective mitigation measure • Wearing of relevant PPE (dust mask and eye
protection) during ash handling
Ash users
6. Disposal of ash and ash containing products
Loss of containment of ash
Preventative mitigation measure • The use of Safety Data Sheet (SDS) where disposal
guidance is provided. • The use of the National Norms and standard for the
assessment of waste for disposal and the Regulations for the classification and management of waste.
Corrective mitigation measure • Clean-up plan to be implemented where ash is not
disposed properly.
Ash users
7. Residual ash stockpiled after closure, decommissioning or change of ownership of user facility
Loss of containment of ash
Preventative mitigation measure • Contractual agreement with ash customers to include
the following clause: "The owner of the facility, including the subsequent owner of the facility will remain responsible for any adverse impacts on the environment and health stemming from stockpiled ash, even after operations have ceased."
Corrective mitigation measure • Land remediation
Ash users
Page 4 of 4
FOR OFFICE USE ONLY
Date Received
Decision Taken Authorised Not authorised (provide reason)
Reference Number