TRIGEN GROUP (PTY) LTD DRAFT ENVIRONMENTAL …€¦ · is an expansion from the approximately 1.5MW...

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TRIGEN GROUP (PTY) LTD DRAFT ENVIRONMENTAL MANAGEMENT PROGRAMME FOR THE PROPOSED ADAPTATION OF AN EFFLUENT WASTE-TO-VALUE PLANT AT THE RCL FOODS FACILITY, MCALISTER ROAD, WORCESTER November 2017 SEC Reference number: 0151011 To be read together with the EMPr authorised in terms of Environmental Authorisation reference number 16/3/3/1/B2/32/1010/15, dated 6th January 2016. PO Box 30134, Tokai, 7966 Telephone: 021 712 5060, Fax: 021 712 5061 Email: [email protected]

Transcript of TRIGEN GROUP (PTY) LTD DRAFT ENVIRONMENTAL …€¦ · is an expansion from the approximately 1.5MW...

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TRIGEN GROUP (PTY) LTD

DRAFT ENVIRONMENTAL MANAGEMENT PROGRAMME FOR THE PROPOSED ADAPTATION OF AN EFFLUENT WASTE-TO-VALUE PLANT AT THE RCL FOODS FACILITY, MCALISTER ROAD,

WORCESTER

November 2017

SEC Reference number: 0151011

To be read together with the EMPr authorised in terms of Environmental Authorisation reference number 16/3/3/1/B2/32/1010/15, dated 6th January 2016.

PO Box 30134, Tokai, 7966

Telephone: 021 712 5060, Fax: 021 712 5061 Email: [email protected]

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TABLE OF CONTENTS

1. DETAIL AND EXPERIENCE OF THE EAP WHO PREPARED THE EMPR ................................................................ 4

2. INTRODUCTION..................................................................................................................................................................... 4

1.1 PROJECT DESCRIPTION......................................................................................................................................................... 4

3. STATUTORY OBLIGATIONS .............................................................................................................................................. 9

4. OBJECTIVES, TARGETS AND MEASURES ...................................................................................................................... 9

4.1. DESIGN PHASE IMPACTS ............................................................................................................................................ 10 4.1.1. Groundwater and Stormwater System Contamination .............................................................................................. 10 4.1.2. Fire, Health and Safety Risk ..................................................................................................................................... 11 4.1.3. Health and Safety Risks and Nuisance Odours – Emissions from Manure and from Digestate Drying ................... 11 4.1.4. Health Risks due to Pests .......................................................................................................................................... 12

4.2. PRE-CONSTRUCTION PHASE IMPACTS .................................................................................................................... 12 4.2.1. Bulk Services Identification ....................................................................................................................................... 12 4.2.2. Permits ...................................................................................................................................................................... 13 4.2.3. Training..................................................................................................................................................................... 13 4.2.4. Construction phase site layout .................................................................................................................................. 13 4.2.5. Working Hours .......................................................................................................................................................... 13

4.3. CONSTRUCTION PHASE IMPACTS ............................................................................................................................ 13 4.3.1. Social Considerations ............................................................................................................................................... 14 4.3.2. Appropriate Machinery ............................................................................................................................................. 14 4.3.3. Waste Management ................................................................................................................................................... 14 4.3.4. Storm water ............................................................................................................................................................... 15 4.3.5. Fire Safety ................................................................................................................................................................. 16 4.3.6. Safety and First Aid ................................................................................................................................................... 16 4.3.7. Air Quality ................................................................................................................................................................ 16 4.3.8. Water Quality ............................................................................................................................................................ 16 4.3.9. Noise and Vibration .................................................................................................................................................. 17 4.3.10. Light Pollution .......................................................................................................................................................... 17 4.3.11. Traffic Control .......................................................................................................................................................... 17

4.4. OPERATIONAL PHASE MITIGATION MEASURES ................................................................................................... 18 4.4.1. Fire, Health and Safety Risk ..................................................................................................................................... 18 4.4.2. Groundwater and stormwater system contamination................................................................................................ 19 4.4.3. Nuisance Impacts on Neighbours .............................................................................................................................. 20 4.4.4. Dust impacts .............................................................................................................................................................. 20

4.5. DECOMMISSIONING PHASE IMPACTS ..................................................................................................................... 20

5. IMPLEMENTATION OF THE EMP ................................................................................................................................... 21

5.1. ROLES AND RESPONSIBILITIES, INCLUDING MONITORING, AUDITING AND REPORTING ..................................................... 21 5.2. DOCUMENTATION AND RECORD KEEPING ......................................................................................................................... 21 5.3. ENVIRONMENTAL AWARENESS AND TRAINING ................................................................................................................. 22 5.4. MATTERS PERTAINING TO NON-CONFORMANCE ONSITE ................................................................................................... 23

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- 3 - List of Annexures

Annexure A Glossary

Annexure B Possible Method Statement Template

Annexure C Role of the Environmental Control Officer (ECO)

Annexure D 1) Site Layout Plan

Annexure E Incident Register and Basic Accident Register Templates

Annexure F Curriculum Vitae’s of EAP’s

IMPORTANT NOTE: ALL READERS TO PLEASE FAMILIARISE THEMSELVES WITH THE RELEVANT TERMINOLOGY

CONTAINED IN THE GLOSSARY (APPENDIX A) PRIOR TO READING THIS DOCUMENT.

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1. DETAIL AND EXPERIENCE OF THE EAP WHO PREPARED THE EMPR

Sillito Environmental Consulting (SEC) has been appointed as the independent Environmental Assessment Practitioner (EAP) to apply for a Waste Licence for the proposed adaptation of an effluent Biodigester plant at the RCL Foods chicken processing facility, McAlister Road, Worcester. This report was prepared by Colleen McCreadie of SEC, and reviewed by Adrian Sillito. Adrian Sillito is a certified environmental assessment practitioner (CEAPSA), Professional Natural Scientist (Pr.Sci.Nat.) and a member of the International Association for Impact Assessment (IAIA). Adrian has over twenty years’ experience in the field of environmental management and impact assessment. Colleen has an Economics Honours degree from UCT and has ten years’ experience in environmental management and impact assessment. She is also a member of IAIA. Please refer to EAP Curriculum Vitae’s contained in Appendix F.

2. INTRODUCTION 1.1 Project Description Introduction The development proposal is for the adaptation of an existing waste-to-value plant, which is situated at the RCL Foods chicken processing plant on Erf 4396, McAlister Road, Worcester Industria. Currently, the waste-to-value plant generates biogas through a process of anaerobic digestion of the effluent sourced from the chicken processing plant. The biogas is then burnt to generate electricity for use by the RCL plant. This EMPr is therefore to be read together with the EMPr authorised in terms of Environmental Authorisation reference number 16/3/3/1/B2/32/1010/15, dated 6

th

January 2016. Figure 1. Site Locality

Expanded Biodigester footprint

RCL Foods site

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- 5 - It is now proposed to include poultry manure from nearby RCL Foods poultry farms and other farms as a feedstock for the waste-to-value plant. This will entail the installation of additional digester tanks and associated infrastructure. The design of the adapted waste-to-value plant will allow for up to 10MW of electricity to be generated, which is expected to power a large majority of the RCL Foods processing facility, including the waste-to-value plant itself. This is an expansion from the approximately 1.5MW currently generated by the effluent digestion plant. Waste heat generated during biogas combustion will also be used to generate steam and hot water for integration back into the processing plant. In addition to this, the manure digestion process generates as a by-product a digestate. This proposal includes the drying of the digestate to produce fertilizer for agricultural applications. Anaerobic digestion process Solid manure will be added to a set of dedicated digestion tanks along with treated effluent outflow from the effluent digestion tanks. The manure digestion tanks are designed to maximise the conversion of the organic matter in the waste to energy-rich biogas for conversion into useful energy. The manure digesters will have the capacity to convert up to 100 ton per day of feedstock. A digestate will be produced as a product of the waste digestion process. This digestate is suitable for use as an agricultural fertilizer. Biogas combustion process The Biodigester will have the capacity to produce approximately 2000m

3/hour of biogas

1, comprising 50-75%

methane; 25-50% carbon dioxide; 0-10% nitrogen; 0-1% hydrogen; 0-3% hydrogen sulphide; and 0-2% oxygen. Compounds in the biogas can cause corrosion and precipitation leading to premature equipment failure. The biogas will be conditioned in a gas treatment unit that employs a process of cooling and filtering to remove these problematic compounds prior to burning. The biogas will be burnt in combined heat and power engines (CHP’s), which have the capacity to combust all of the biogas produced by the digesters. The electricity produced – up to 10MW - is expected to be sufficient to power the majority of the RCL plant. The waste heat produced will supplement some of the coal energy supply currently used at the coal fired boilers on the site. The plant is anticipated at this stage to include at least five CHP engines. Waste The biodigestion process will produce approximately 80 tonnes per day of digestate as a waste product, which will be dried and pelletized on site. The digestate is appropriate for agricultural fertilizer applications and so will be returned to the RCL poultry farms and other agricultural users for this purpose. Digestate drying will take place by means of a closed-system conveyer belt dryer either fuelled by biogas, or using waste heat from the CHP engines. Water recovery process An additional adaptation to the current waste-to-value plant is the installation of a water recovery plant. A portion of the treated effluent discharged from the effluent digesters will be used to feed the water recovery plant. This plant will treat the treated effluent using a specialised Reverse Osmosis (RO) membrane system designed for high fouling applications. The feed will be separated into a high quality permeate stream and high strength brine stream which will be blended back into final effluent not treated by the water recovery plant. The RO plant will consist of the following pre-treatment steps: gravity settling, sand filtration, cartridge filtration. Post treatment steps will include flash aeration to remove volatiles and disinfection. Settling, filtration and aeration will take place in a series of bulk tanks. Recovered water produced will be returned to the factory to reuse at suitable points and applications.

1 The biogas is continuously piped to the CHP engine so that at any one time, only up to 500m

3 of storage capacity for the biogas

is required.

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- 6 - This represents a reduction in the quantity of effluent currently being discharged to municipal sewer; as well as a reduction in water usage at the chicken processing plant. Infrastructure Infrastructure required will be as follows:

1) Digestion tanks for the anaerobic digestion of the manure to produce biogas. 2) An enclosed, purpose-designed structure for the offloading and storage of the manure for up to three days.

The unit will include a receiving bay in which the doors will only be opened during a manure delivery. 3) The manure storage structure will operate under negative pressure, with air extracted to a filtration system for

removing odorous emissions prior to exhausting to atmosphere. 4) The filtration system will be a chemical scrubber (sulphuric acid) aimed at scrubbing the ammonia rich

exhaust gas from the storage unit. 5) A closed storage tank for the digestate from the manure digestion. 6) A closed-system conveyer belt drier for drying the digestate. 7) At least five Combined Heat and Power (CHP) engines. 8) A series of tanks for water recovery – for gravity settling, filtration, RO and flash aeration. 9) Pipelines for the conveyance of manure; digestate; treated effluent; hot water; processed water; biogas and

steam. 10) Distribution lines for electricity.

There will be no need for additional connections to the municipal water or electricity supply network; or to the municipal sewerage or stormwater systems. The plant will utilise the existing site access off McAlister Street, with the traffic generated by the delivery of manure expected to be up to 5 trucks per day, i.e. a negligible increase in traffic given activities taking place in the surrounding industrial area. It is expected that these same delivery trucks once empty will be loaded with the dried digestate to transport the fertilizer to agricultural users. These trucks will be covered to prevent rainwater ingress and odour emissions.

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- 7 - Figure 2, Process Flow Diagram

CHICKEN PROCESSING PLANT/ ABATTOIR & BY-PRODUCTS

RENDERING PLANT

BIODIGESTERS

(CHP) ENGINES

BIOGAS UP TO 2000M3/HR GENERATED; UP TO 500M3

STORAGE REQUIRED

PROCESSED CHICKEN

MEAL (FOR USE IN DOG FOOD, ETC.)

WASTE HEAT

EFFLUENT UP TO 15 000KL/DAY

ELECTRICITY UP TO 10MW GENERATED

COMBUSTION GASES (CO2, SO2, NOx, water vapour) +-

2128KG/HR CO2

EMERGENCY FLARE COMBUSTION GASES (CO2,

SO2, NOx, water vapour)

RCL BROILER FARMS & OTHER FARMS

RCL PLANT

MANURE UP TO 100T/DAY

WASTE: DIGESTATE (FERTILIZER) UP TO 80T/DAY

STEAM HOT WATER

TREATED EFFLUENT

AGRICULTURAL USERS INCL. RCL BROILER FARMS

MUNICIPAL WWTWDIGESTATE DRYING PLANT

FERTILIZER

MANURE STORAGE & DIGESTATE DRYING EMISSIONS SCRUBBER

(H2SO4)

SCRUBBER EFFLUENT (AMMONIUM SULPHATE

SOLUTION)

2.1. Aspects Covered by this EMP The development proposal entails the construction and operation of additional Biodigesters and associated infrastructure as described above. The potentially significant impacts identified during the EIA process as being associated with the facility are as follows: Construction and decommissioning phases:

1) Natural stormwater drainage channel contamination from contaminated liquid surface spillages 2) Dust 3) Traffic and access 4) Fire, health and safety risk 5) Noise

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- 8 - Operational phase:

1) Groundwater and stormwater system contamination 2) Fire, health and safety risk 3) Health and safety risks and impacts on wellbeing from emissions form manure storage and digestate drying 4) Health risks from pests (flies), which can spread pathogens associated with manure storage and handling

Figure 3. Risks Identified with Operating the Waste-to-Value Plant

CHICKEN PROCESSING PLANT/ ABATTOIR & BY-PRODUCTS

RENDERING PLANT

BIODIGESTERS

COMBINED HEAT & POWER (CHP) ENGINES

BIOGAS UP TO 2000M3/HR GENERATED; UP TO 500M3

STORAGE REQUIRED

PROCESSED CHICKEN

MEAL (FOR USE IN DOG FOOD, ETC.)

WASTE HEAT

EFFLUENT UP TO 15 000KL/DAY

ELECTRICITY UP TO 10MW GENERATED

COMBUSTION GASES (CO2, SO2, NOx, water vapour) +-

2128KG/HR CO2

EMERGENCY FLARE COMBUSTION GASES (CO2,

SO2, NOx, water vapour)

RCL BROILER FARMS & OTHER FARMS

RCL PLANT

MANURE UP TO 100T/DAY

WASTE: DIGESTATE (FERTILIZER) UP TO 80T/DAY

STEAM HOT WATER

TREATED EFFLUENT

AGRICULTURAL USERS INCL. RCL BROILER FARMS

MUNICIPAL WWTWDIGESTATE DRYING PLANT

FERTILIZER

RISK: ammonia

emissions - nuisance

odours; occupational

health

RISK: gas leak &

combustion source:

fire & explosion

RISK: large-scale,

long-term exposure

to soil & stormwater:

contamination

RISK: gas leak &

combustion source:

fire & explosion

RISK: spill or leak:

soil, groundwater &

stormwater system

contamination

RISK: equipment failure:

excessive atmospheric

emissions causing pollution

RISK: equipment

failure: fire &

explosion; noiseRISK: ammonia

emissions - nuisance

odours; occupational

health

MANURE STORAGE & DIGESTATE DRYING EMISSIONS SCRUBBER

(H2SO4)

SCRUBBER EFFLUENT (AMMONIUM SULPHATE

SOLUTION)

In order to minimise any negative impacts associated with the facility, therefore, it is imperative that the lifecycle of the facility, as well as all aspects of the facility’s development (infrastructure) and operation (processing, storage, and handling) are subject the conditions set out in this EMP. The conditions directly address the identified potential impacts, in order to ensure that the health, safety and environmental risks associated with the plant can be avoided or minimised.

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- 9 - 2.2. Map of Environmental Sensitivities Erf 4396, where the effluent digester plant is situated which is proposed for adaptation, is a heavily transformed site which has been used for industrial purposes for decades. There are therefore no sensitive areas on the site which need to be avoided. The site layout plan contained in Appendix D shows the proposed layout of the plant on the site. 2.3. Legal Framework

This Environmental Management Programme (EMP) has been compiled in fulfilment of the requirements of Section 24N of the National Environmental Management Act, Act No. 107 of 1998 (as amended) (NEMA).The contents of this EMP comply with the requirements for EMP’s as contained in Appendix 4 to the 2014 EIA Regulations. The EMP should also adhere to the local authority by-law requirements as well as any other obligatory environmental and other legal requirements (see Section 3 of this EMP). Changes to this Environmental Management Programme can only occur with the written approval of the DEA&DP and an updated version should also be forwarded to all parties once the amended EMP has been approved by the DEA&DP. It is understood that the Trigen Group (Pty) Ltd or any future development entity (where transfer of ownership occurs) will be fully responsible for this EMP and its requirements including any environmental rehabilitation that may be needed. This is required in terms of Section 28 (Duty of Care and Remediation of Damage) of the National Environmental Management Act, (Act No. 107 of 1998), as amended.

3. STATUTORY OBLIGATIONS The applicant should adhere to any statutory requirements which may be relevant to the lifecycle of the biodigester

facility, contained in:

The National Environmental Management Act, Act 107 of 1998, as amended (NEMA).

National Water Act, Act 36 of 1998, as amended.

National Environmental Management Waste Act, Act 59 of 2008

The National Environmental Management Air Quality Act, Act No. 39 of 2004

All relevant by laws and building regulations of the Breede Valley Local Municipality

All relevant by laws and building regulations of the Cape Winelands District Municipality

Relevant SANS codes

The Operational Health and Safety Act, Act 85 of 1993.

4. OBJECTIVES, TARGETS AND MEASURES A variety of potential impacts are associated with the operation of the biodigestion facility. A number of mitigatory measures are proposed to minimise impacts during the operational phase. It is understood that the applicant, the Trigen Group (Pty) Ltd, is responsible for any environmental rehabilitation as identified. It is understood that the applicant, the Trigen Group (Pty) Ltd, is responsible for the implementation of the recommended impact management measures throughout the lifecycle of the development; as well as being responsible for any environmental rehabilitation as identified.

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- 10 - 4.1. DESIGN PHASE IMPACTS Timeframe for implementation of design phase measures: The design of the development proposal is aimed at minimisation of health, safety and environmental risks associated with the plant. These design-phase measures must therefore be implemented at the earliest stages so that construction works can proceed in line with these measures.

4.1.1. Groundwater and Stormwater System Contamination Objectives: To prevent contamination of groundwater or stormwater as a result of a spillage, tank or line leak and surface runoff of untreated effluent or acids from the nutrient dosing tank farm; or from manure storage on bare soil or uncontrolled rainwater runoff from manure. Targets: To comply with relevant codes of practice and applicable legislation with respect to prevention of pollution of natural resources. Measures: The acid storage facility must be designed with the following measures in place:

(a) All process tanks and pipework, and the chemical (nutrient dosing) tank farm to be designed and constructed according to the relevant codes of practice, including:

i. API STD 620 – recommended rules for design and construction of low pressure tanks ii. AWWA D103 – design, construction, inspection and testing of factory coated steel bolted

tanks iii. AWWA D100 - design, manufacture and procurement of welded carbon steel tanks iv. BS2594 - specification for carbon steel welded horizontal cylindrical storage tanks v. BS2654 - manufacture of vertical steel welded storage tanks with butt welded shells vi. SANS 1476 - Fabricated flanged steel pipework, pipe and fittingsSANS310 - storage tank

facilities for hazardous chemicals) vii. BS 8007 - design of concrete structures for retaining aqueous liquids viii. SANS 10100 - the structural use of concrete ix. SANS 10162 - the structural use of steel x. SANS 10108 - the classification of hazardous locations and the selection of equipment for

use in such locations xi. SANS 62305 – protection against lightning

(b) The manure storage unit should be purpose designed to provide adequate containment of the manure – to prevent contact with soil and to prevent rainfall ingress. Offloading of the manure should take place within the controlled receiving bay of the storage unit.

(c) The storage unit design is to include reinforced concrete floors.

(d) Wash down water from the storage unit will be fed to the anaerobic digester,

(e) A groundwater and surface water monitoring programme should be compiled in detail in conjunction with the Breede-Gouritz Catchment Management Agency. Based on preliminary feedback from the BGCMA, for the first two years after plant commissioning, the programme may include monitoring of nearby drainage channels during the high flow season; and sampling for the following parameters should be undertaken: pH; electrical conductivity; COD; ammonia; nitrates and nitrites; phosphates. In addition, the programme may include the requirement to sample at the existing borehole on Erf 4396.

(f) Control of surface runoff in such a manner that spillages can be contained and so prevent access to the stormwater system. This must be achieved through appropriate secondary containment.

(g) An Emergency Response Plan must be compiled for the plant, to include response to tank, line or bund failure.

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- 11 - (h) A stormwater management diagram must be compiled during the detailed design phase and must

identify and show nearby stormwater channels; and demonstrate adequate control of surface runoff from the site to cater for flood events. The diagram must be approved by the Breede Gouritz Catchment Management Agency prior to construction commencing.

4.1.2. Fire, Health and Safety Risk

Potential health and safety impacts associated with the risk of fire and explosion are associated with methane gas storage. Associated smoke and disturbance related to with the evacuation of the site and surrounding area; risk to life and property. Objectives: To minimise risk through adequate design and operational measures. Targets: To meet best practice design and operational measures

(a) SANS10108: Classification of hazardous locations and SANS 60079-14: Explosive atmospheres electrical installations design, selection and erection must be adhered to in the design and construction of the plant.

(b) An Emergency Response Plan must be compiled for the plant. This will be developed once the final installation plan has been developed, a HAZOP study has been undertaken and all risk management issues addressed and adopted into the final scheme.

(c) The RCL facility is currently a Major Hazard Installation. Once the manure Biodigester has been

commissioned, the MHI for the plant should be updated. (d) Sufficient & suitable storage of flammables must be provided (e) Sources of ignition must be avoided wherever flammable or highly combustible material is present in the

workplace e.g.: i. Notices prohibiting smoking is displayed and enforced ii. Welding and flame cutting is only allowed under controlled conditions that includes written

hot work permits iii. Only spark-free hand and power tools are used iv. No grinding, cutting and shaping of ferrous metals are allowed using electrically driven

power tools that produces sparks

(f) Flameproof switches & fittings are to be used in the flammable atmosphere

(g) Overfill protection devices must be installed.

4.1.3. Health and Safety Risks and Nuisance Odours – Emissions from Manure and from Digestate Drying

Objectives: To avoid nuisance odorous emissions impacting on people’s wellbeing; and to minimise health and safety risks for workers due to harmful emissions. Targets: To comply with relevant ambient air quality standards and occupational exposure limits for compounds of concern. Measures:

a) Fully enclosed, moving-bed trucks should be used to transport the manure and dried digestate to and from site.

b) The service contract between the applicant and the manure suppliers should stipulate that the logistics provider must maintain the trucks in a sanitary condition.

c) The manure storage unit and the digestate drier should be purpose designed to provide adequate containment of the manure and digestate to prevent fugitive odorous emissions.

d) Manure should be stored for a period of up to 3 days to prevent anaerobic and aerobic breakdown of the

manure.

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e) The storage unit requires an appropriate ventilation and extraction system to ensure indoor air quality that complies with all relevant occupational exposure limits.

f) Operators must wear personal gas monitors to detect dangerous gas concentrations.

g) Breathing apparatus will be positioned at critical points in the storage facility.

h) The ventilation and extraction system for the storage unit requires an appropriate abatement system to ensure

that odorous exhaust gases are treated prior to venting to atmosphere.

i) The abatement system is to comprise a chemical scrubber (sulphuric acid), designed by a registered professional engineer.

j) The scrubber design is to allow for possible future adaptations or upgrades that may be required in order to ensure that odours are minimised.

k) The detailed design of the scrubber is to be submitted to the Cape Winelands District Municipality’s air quality officer for approval prior to plant commissioning.

l) If nuisance odours are emitted from the digestate drier, the exhaust gas from the drier should be tied into the

chemical scrubber at the manure storage unit.

m) Offloading of the manure should take place within the controlled receiving bay of the storage unit. Receiving bay doors to remain closed except during a manure delivery.

See Appendix B for preliminary design drawings for the extraction and abatement system.

4.1.4. Health Risks due to Pests Objectives: To avoid spread of disease from pests attracted to manure storage and handling. Targets: To implement adequate pest control measures at the manure storage unit. Measures:

(a) Please refer to measures under Section 4.1.3

(b) In addition, the manure storage unit floors will be designed so as to prevent pooling of wash water. (c) The storage unit will be cleaned regularly according to a cleaning schedule and work instruction. (d) A Pest Management Plan should be compiled within 6 months of the plant being commissioned.

4.2. PRE-CONSTRUCTION PHASE IMPACTS Timeframe for implementation of pre-construction phase measures: Prior to any construction activities taking place, the following measures will need to be complied with:

4.2.1. Bulk Services Identification Objectives: To minimise any possible damage to existing bulk services as a result of pre-construction and construction related activities. Targets: To comply with any local authority by-laws regarding bulk services and to avoid additional costs and potential project delays due to damage to these services Measures:

If any bulk services are required to be relocated and/or rerouted then the appropriate permits/approvals must be sought.

The location of existing bulk services must be determined to prevent accidental damage to these facilities.

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4.2.2. Permits Objectives: To ensure that the necessary permits regarding any activities related to construction activities are in place prior to construction starting. Targets: To ensure that the construction works can proceed without possible delays and/or legal repercussions during building works as a result of outstanding permits and/or non-compliance with permits. Measures:

The client shall issue a list of applicable permitting conditions together with the respective permits/authorisations to the ECO prior to the start of construction works.

4.2.3. Training

Objectives: To ensure that all staff working on site are adequately trained on the requirements of this EMP and are legally compliant with relevant legislation. Targets: To ensure that the requirements of this EMP are understood and implemented by all staff (as and when required) on site. Measures:

The ECO will provide for site contractor management training sessions (as required), who will in turn ensure that all staff working on site are familiar with the workings and requirements of this EMP

An interpreter should be provided as required.

4.2.4. Construction phase site layout Objectives: To designate areas on site for various types of construction related activities. Targets: To ensure an efficient and orderly layout that promotes safe access Measures:

The location of storage areas for any construction materials must be agreed to by the ECO, Principal Agent and Contractor prior to the commencement of work at the site.

A sketch diagram of the above is required by the ECO.

This area must all be kept tidy, sanitary and in good condition throughout the project.

4.2.5. Working Hours Objectives: To designate working hours for construction related activities. Targets: To ensure that the hours of operation shall be restricted to those stipulated by the local authority. Measures:

The contractor shall at all times ensure that working hours are restricted to those stipulated by the local authority.

Modifications to the above may only take place through the local authority and the ECO must be notified in writing.

4.3. CONSTRUCTION PHASE IMPACTS

Timeframe for implementation of construction phase measures: The construction phase measures for minimisation of any health, safety and environmental risks need to be adhered to throughout the construction phase of the project.

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4.3.1. Social Considerations Objective: To minimise social impacts (e.g. nuisance factors) related to the construction of the site through effective communications with abutting neighbours. Targets: To ensure compliance with the local authority by-laws and any other statutory requirements relating to site construction and demolition impacts. Measures:

All abutting neighbours (or as required) must be notified of the proposed construction phase activities at least two weeks before they commence.

The Contractor must record and repair any damage that the construction works may cause to neighbouring properties.

The ECO must be notified in writing of any incidents relating to the above.

4.3.2. Appropriate Machinery Objectives: To minimise possible nuisance affects and environmental damage through the use of appropriate machinery during the construction works. Targets: To ensure that impacts and damage to the environment are minimised via the responsible use of appropriate machinery on site. Measures:

The Contractor shall at all times carefully consider what machinery is appropriate to the task in the context of this EMP while minimising the extent of environmental impact.

A dedicated parking area must be defined with drip trays beneath any potentially leaking equipment and fuel/lubricant absorbing media (peat/moss type products) within these drip trays must be used to contain any spilled liquids.

These materials must be replaced regularly to prevent over-saturation and potential spillage of free phase product. This material must be disposed of as hazardous waste and be collected by an approved Contractor/delivered to a suitable landfill site.

Chain of custody documentation must be provided as proof of final end recipient.

All spills are to be recorded in the Environmental Register, including any clean-up actions taken to remediate the spillage. Such actions are to be agreed with the ECO prior to taking place.

4.3.3. Waste Management

Objectives: To minimise possible environmental damage through inappropriate waste management on site or related to the site. Targets: To ensure that the handling of waste is in accordance with the statutory requirements of the local authority by-laws and the National Environmental Management Waste Act, Act 59 of 2008. Measures: 1) Liquid Waste:

Liquid dispensing receptacles (e.g. lubricants, diesel, shutter oil etc.) must have drip trays beneath them/beneath the nozzle fixtures.

A spill management protocol must be produced by the Contractor and approved by the ECO prior to works commencing on site.

Material safety data sheets (MSDS) must be available on site where products are stored, so that in the event of an incident, the correct action can be taken.

Depending on the types of materials stored on site, suitable product recovery materials (such as Spillsorb or Drizit products) must be readily available.

Cement contaminated water must be fed to a container, neutralised and suitably disposed of (e.g. sent to a suitable landfill site). In the latter case, chain of custody documentation must be provided to ensure a suitable end recipient. The latter must be kept with the environmental register.

The Contractor shall ensure that any wastewater generated during construction activities feeds to a suitable containment area such as a container or lined sedimentation pond prior to disposal. This pond or ponds must be allowed to dry out on a regular basis to allow for solid material removal. The wastewater must be disposed of in a suitable manner (possibly to the sewer system following local authority approval) and must not be directed to a storm water drain.

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Storm water must be managed in such a way that no overland flow is possible onto any area of the site which could contain potential contaminants (such as concrete mixing areas, material and hazardous storage areas from any adjacent area).

2) Solid Waste:

Waste must be categorised by the Contractor and disposed of in a suitable manner into separate waste streams (this includes general, hazardous and recyclable waste) only at authorised waste disposal facilities.

The Contractor must provide an adequate number of waste receptacles for general waste at points around the construction site as well as for hazardous and recyclable waste.

Waste is to be collected either by the Municipality or via a licensed waste disposal Contractor.

The frequency of collections/emptying of waste receptacles will be of such a frequency that waste receptacles do not overflow.

Particular care shall be taken with the disposal of materials that could be wind-borne or waterborne to ensure that the release of these materials is minimised (the latter is a requirement for hazardous waste).

The use of netting covers or similar sealed containers must be implemented as and when required by the ECO.

All material used by the Contractor during the construction phase shall be managed in such a way that it does not cause pollution, or that it minimises pollution. In the event of a spillage, the Contractor should have suitably trained personnel who can correctly clean up any spillage in an efficient and environmentally sound manner.

3) Hazardous Waste:

Storage areas that contain hazardous substances must be covered and bunded with an approved impermeable liner or have some form of secondary containment.

The Contractor shall keep MSDS on-site for all potentially hazardous materials used.

Suitably trained personnel shall be available on the site during working hours so that in the event of human exposure to any hazardous materials that the correct first aid actions are taken. This training should also include environmental spill containment procedures

Spills in bunded areas must be cleaned up, removed and disposed of safely from the bunded area as soon after detection as possible to minimize pollution risk and reduced bunding capacity.

Chain of Custody documentation must be provided for any hazardous substances disposed of as proof of end recipient and disposal at an authorised hazardous waste disposal facility.

4) Cement/concrete mixing areas:

Cement powder has a high alkalinity, which can contaminate and dramatically affect both soil and groundwater. The following recommendations are made:

Mixing areas must be defined on site and approved by the ECO.

No mixing of cement is allowed on bare soil and a lined bund or bunded portable mixer must be used. The use of ready mix concrete must be considered.

Cement bags must be disposed of in demarcated hazardous waste receptacles and the used bags disposed of via the hazardous substances waste stream.

Excess or spilled concrete must be disposed of to a suitable landfill site, with chain of custody documentation provided.

4.3.4. Storm water

Objectives: To minimise potential impacts arising out of improper management of storm water originating on site. Targets: To ensure that storm water on site is managed according to the local authority by-laws and in accordance with any other statutory requirements and that no negative impacts occur to the storm water services around the site. Measures:

Storm water outfalls should be designed to reduce flow velocity and avoid downstream erosion.

Soil erosion on site must be prevented at all times.

If the storm water is of such a quality that suspended solids are present then detention ponds for removal of suspended solids must be considered.

During construction, all material excavated must be protected, screened or covered to prevent off site movement (primarily wind-blown soil or surface runoff) and the surplus material must be removed from site weekly to a licensed waste disposal site or re-used if appropriate.

All storm water channels around the outside of the site should be inspected regularly to ensure that they are not blocked and/or obstructed to ensure their efficient operation.

Storm water runoff must be controlled to ensure that on-site activities do not result in off-site pollution.

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4.3.5. Fire Safety Objectives: To prevent any potential impacts related to fires originating on site. Targets: To ensure compliance with the local fire department and local authority by-laws and any other statutory requirements relating to fire safety. Measures:

Adequate training in emergency response situations of the contractor and construction personnel undertaking the construction activities will be carried out.

Firefighting facilities which will include hand-held fire extinguishers and a hose reel. These facilities must be approved by the local fire department.

Minimisation of hot work by using alternative methods and equipment such as air driven tools, cold cutting and pre-fabrication off site.

The use of appropriate shielding and screening such as blanketing with firefighting foam and water screens to minimise fire risk.

Minimisation of spark quenching by wetting down and/or using construction power tools such as jack hammers under running water.

A fire attendant will be on stand-by during the construction process.

4.3.6. Safety and First Aid Objectives: To minimise any potential safety or health related incidents on site. Targets: To ensure compliance with the local authority by-laws and any other statutory requirements relating to health and safety on a construction site. Measures:

All people working on site are responsible for their own safety on site. Contractors and Principal Agent/s shall at all times comply with the relevant statutory requirements including the Occupational Health and Safety Act, Act No.85 of 1993.

A comprehensive site specific first aid kit must be available on site at all times.

At least one person trained in safety and first aid and familiar with the first aid equipment on site must be present on the site at all times.

Emergency procedures must also be established prior to the start of construction operations on site and appended to this EMP.

4.3.7. Air Quality

Objectives: To minimise potential air quality impacts during construction related activities. Targets: To ensure compliance with the local authority by-laws and any other statutory requirements relating to air quality. Measures:

Wind-blown dust and sand may generate considerable negative impacts (e.g. reduced visibility for vehicles travelling along adjacent roads and nuisance to neighbours/adjacent erven). The use of water bowsers and wetting down of loose soil areas, as well as the erection of shade netting screens to prevent off-site movement of dust is required and/or other appropriate action to minimise this impact.

The use of straw stabilisation or mulching of exposed sandy areas may also be considered in consultation with the ECO.

Water for dust suppression is to be sourced from non-potable sources as far as possible, e.g. the contractor can erect a rainwater harvesting tank on the site; and/or if there is a settlement pond on the site for excess cement mixing water runoff, the top layer of mixing water – where the fines have settled out – can be utilised for dust suppression

4.3.8. Water Quality

Objectives: To minimise any potential impacts on the groundwater quality at and off site through indirect impacts. Targets: To ensure compliance with the local authority by-laws and any other statutory requirements relating to water quality.

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- 17 - Measures:

Site staff shall not be permitted to use any stream, river, open water body or natural water source adjacent to or within the designated site for the purposes of bathing, washing of clothing, or for any construction or related activities.

Measures to control illegal dumping of construction waste must be implemented to prevent pollution to surface water run-off.

4.3.9. Noise and Vibration

Objectives: To minimise any potential noise impacts related to the construction operations on site. Targets: To ensure compliance with all legal requirements, including the local authority by-laws and any other statutory requirements relating to noise impacts. Measures:

The Contractor must use appropriate, modern equipment, which produces the least noise.

The use of noise shielding screens should be considered by the project team as and when required.

The provisions of SABS 1200A Sub clause 4.1 regarding "built-up areas" shall apply to all areas within audible distance of residents whether in urban, peri-urban or rural areas.

No amplified music shall be allowed on site. The use of radios, tape recorders, compact disc players, television sets etc. shall not be permitted unless the volume is kept sufficiently low as to avoid any intrusion on members of the public within range.

The Contractor shall not use sound amplification equipment on site unless for the purposes of site safety and communications and in emergency situations.

Construction activities shall be confined to the hours stipulated by the local authority.

The Contractor will issue ear protection for any noise activities with a noise output of 85 dB or more.

The Contractor must notify all adjacent property owners/occupants of the proposed development and that noise impacts above 85 dB may occur as a result of the above.

No noise generating work is to be conducted outside of approved working hours unless in consultation with the local authority and advised to the adjacent property owners/occupants prior to works taking place.

4.3.10. Light Pollution

Objectives: To minimise light impacts associated with construction related activities. Targets: To ensure that light pollution is minimised such that no complaints are received from the public. Measures:

All legal requirements will be complied with to ensure that impacts are minimised.

Any lighting required by the Contractor shall be aimed at the area to be lit on site and the over spillage must be kept to a minimum.

4.3.11. Traffic Control Objectives: To ensure that traffic impacts as a result of the construction related activities are minimized. Targets: To ensure compliance with the local authority by-laws and any other statutory requirements relating to construction traffic. To ensure that the impacts on current traffic flows in the vicinity of the site are minimised and that complaints relating to traffic associated with the site’s activities are minimised. Measures:

Appropriate traffic routing and scheduling of construction related vehicles will be carried out in consultation with a competent traffic engineer.

The contractor must provide a competent traffic marshal for situations where heavy construction traffic may impede normal traffic flows on any roads adjacent to the site.

All vehicles will be legally compliant.

All drivers will be competent and in possession of an appropriate valid driver’s license.

All vehicles travelling on site will adhere to the specified speed limits.

The movement of all vehicles will be controlled such that they remain on designated routes.

No member of the workforce will be permitted to drive a vehicle under the influence of alcohol or narcotic substances.

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4.4. OPERATIONAL PHASE MITIGATION MEASURES Timeframe for implementation of operational phase measures: The measures for minimising health, safety and environmental risk associated with operations at the new plant, will need to be implemented on an on-going basis throughout the operational lifespan of the development.

4.4.1. Fire, Health and Safety Risk Potential health and safety impacts associated with the risk of fire and explosion are associated with methane gas storage and acid storage. Associated smoke and disturbance related to with the evacuation of the site and surrounding area; risk to life and property. Objectives: To minimise risk through adequate design and operational measures. Targets: To meet best practice design and operational measures. Measures:

(a) The safety of workers is of paramount importance. All workers and managers on site must be sensitised about the safety risks that exist at the plant in terms of fires, vapour cloud explosions and the release of toxic vapours. Workers and management must be trained in the safety and emergency response procedures that apply to the factory and its premises. Regular breathalyser tests must be conducted on site among all workers and management to ensure that no worker consumed alcohol before entering the site or while present on the site. If any worker or manager fails the breathalyser test, he/she must be dismissed with immediate effect.

(b) A specific person must be appointed in accordance with Section 16 (2) of the Occupational Health and Safety Act to take responsibility, together with the appointed Chief Executive Officer, for the health and safety of all workers on site. This safety officer must have the authority to stop any work or action that may pose a health and safety threat to other workers on site.

(c) All fire extinguishers on the premises must be tested at least once every six months by a certified equipment supplier.

(d) All drums and flow bins that contain flammable liquids must be stored in a bunded area. (e) Trigen must ensure that sufficient people are employed to ensure the safe and reliable operation of the

proposed biodigester plant and to have adequate human resources available to manage any emergency situation that may occur at the chemical plant.

(f) Sources of ignition must be avoided wherever flammable or highly combustible material is present in the

workplace e.g.: i. Notices prohibiting smoking is displayed and enforced ii. Welding and flame cutting is only allowed under controlled conditions that includes written

hot work permits iii. Only spark-free hand and power tools are used iv. No grinding, cutting and shaping of ferrous metals are allowed using electrically driven

power tools that produces sparks (g) Good housekeeping must be maintained to prevent the accumulation of unnecessary combustibles.

(h) Adequate ventilation must be maintained. (i) Gas flow to be shut off immediately at source (if safe to do so) during incident. (j) Adequate and suitable fixed and portable fire appliances must be provided and maintained in good

working order. Maintenance must include: i. Regular inspection by a competent person appointed in writing and keeping a register ii. Annual inspection and service by an accredited service provider

(k) Emergency escape routes must be kept clear at all times.

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(l) Evacuation must be practised to ensure that all are evacuated timeously. (m) Roll call must be held after evacuation to account for all personnel and ensure that no one has been left

behind. (n) Adequate training of management and employees in emergency response situations must be carried out. (o) Preventative maintenance must be done on equipment on a regular basis.

(p) Disciplinary action must be instituted immediately against any worker or member of management that

contravenes the safety rules applicable to the premises. (q) The management of RCL Foods must report all safety incidents, including near misses, to the Chief of the

Fire Department as well as to the Provincial Director of the Department of Labour. (r) An Incident and Accident Register must be kept at the site. Please refer to Annexure G for example

templates. (s) A Health and Safety Committee must be instituted at the factory. The Committee must meet at least once

per month for a review of the safety conditions and status at the premises.

4.4.2. Groundwater and stormwater system contamination

Contamination of groundwater and stormwater as a result of a spillage, tank or line leak and surface runoff of untreated effluent into the stormwater system. Objectives: To ensure that any spills or leaks at the site from an incident or from day-to-day storage and handling activities, are not able to reach groundwater or the stormwater system. And in the event of an incident, that prompt action is taken to remedy the cause of the spill or leak and to address any potential contamination. Targets: To comply with best practice and legislative requirements. Measures: (a) Stock reconciliation must be undertaken regularly to identify any leaks.

(b) Any incident that results in ingress of untreated effluent or similar into the soil and potentially the groundwater

and or stormwater system must be reported to all relevant authorities, including DEA&DP and the Breede Gouritz Catchment Management Agency on behalf of the Department of Water Affairs, within 14 days. This is in compliance with Section 30 (10) of the NEMA and Section 20 (3) of the Water Act. The incident report must include the containment and clean-up procedure and the remediation procedure for the impacted area. Containment, clean-up and remediation must commence immediately.

(c) Hazardous and general waste must be separated. All hazardous waste must be disposed of at a licensed hazardous waste disposal site, with chain of custody documentation retained in the Environmental Register as proof of end recipient.

(d) A spill response kit appropriate to the liquids stored, handled and processed at the site must be kept at the site at all times.

(e) In the event of a spill or leak, spill response according to the Emergency Response Plan must be implemented.

(f) An Environmental Register must be kept on site. The Incident and Accident Registers may be kept in the Environmental Register. Details of any incidences which may occur, as well as details on how the incident was rectified and / or remediated, must be included in the register. The register should also include chain-of custody receipts from disposal of hazardous waste; copies of any Section 30 Incident Form which may need to be sent to the authorities in the event of an incident; results of any on-going monitoring; details of complaints from neighbouring parties with respect to nuisance impacts such as noise or odours; etc. The Environmental Register should be kept updated by the designated site Safety Officer.

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4.4.3. Nuisance Impacts on Neighbours Objectives: To ensure that adjacent occupants and owners are not impacted negatively by nuisance impacts such as noise and odours. Targets: To comply with authority requirements with respect to minimising and managing nuisance impacts on neighbours. Measures: (a) All windblown litter must be collected on site and may not cause a nuisance to neighbours.

(b) Any incident that causes noise, odours or any other nuisance must be rectified within 24 hours from the time

the incident has occurred.

(c) Relevant legislation pertaining to allowable noise levels in an industrial area must be adhered to.

(d) Noise proof containers must be utilised for the noisiest equipment to ensure compliance with relevant legislation pertaining to noise disturbance.

4.4.4. Dust impacts A possible source of dust associated with the Biodigester plant is the storage and handling of manure and digestate. There will be no sandy site surfaces once the plant has been constructed and so vehicle-entrained dust is not expected to be a dust source. Manure will be offloaded from and loaded onto delivery trucks, as well as stored, in an enclosed unit; and dried digestate will be stored and handled in a weather proof unit. Dust is therefore not expected to be an impact of any significance. 4.5. DECOMMISSIONING PHASE IMPACTS

Timeframe for implementation of decommissioning-phase measures: The measures recommended for minimising health, safety and environmental risk associated with the decommissioning of the plant, need to be implemented during the practical decommissioning of the plant. Any rehabilitation measures required will take place for the duration recommended by the specialists compiling the rehabilitation action plan. In the unlikely event that the facility is decommissioned, the construction phase management measures contained in Section 4.3 of this EMP must be implemented.

In addition, the following measures should also be implemented to minimise the health, safety and environmental risks associated with the decommissioning of the infrastructure: (a) Adequate training in emergency response situations of the contractor and construction personnel undertaking

the decommissioning activities will be carried out.

(b) Fire fighting facilities which will include hand-held fire extinguishers and a hose reel. These facilities must be approved by the local fire department.

(c) Minimisation of hot work by using alternative methods and equipment such as air driven tools, cold cutting and pre-fabrication off site.

(d) The use of appropriate shielding and screening such as blanketing with fire fighting foam and water screens to minimise fire risk.

(e) Minimisation of spark quenching by wetting down and/or using construction power tools such as jack hammers under running water.

(f) Use of gas testing at methane gas and acid storage area to ensure there are no residual emissions.

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(g) A fire attendant will be on stand-by during the decommissioning process 5. IMPLEMENTATION OF THE EMP 5.1. Roles and Responsibilities, including Monitoring, Auditing and Reporting

Environmental Control Officer (“ECO”) (a) The ECO must be appointed immediately after licensing of the facility and prior to commencement of any

construction required in order to implement the design requirements for the site.

(b) The responsibilities of the ECO will include monitoring of compliance with the EMP by the applicant and any sub-contractors.

(c) The ECO has the authority to recommend the cessation of works or any portion of construction related activity to the applicant during the tank installation phase. This will be triggered if in his/her opinion the activity has caused or will imminently cause significant damage and/or harm to the environment or is in contravention of the relevant environmental legislation/permits/authorisations applicable to the site and/or activity/ies.

(d) If the applicant fails to show adequate consideration to the EMP or the recommendations of the ECO, then the ECO may recommend to the authorities that the aspect of operations to which non-compliance relates, ceases until the non-compliance is adequately rectified.

(e) At the frequency determined by the licensing authority, the site should be audited against the conditions of the EMP and the Waste Licence by an independent ECO. The audit reports should be submitted to the DEA&DP and both the Local and District Municipality for their records.

(f) Audit reports must contain monitoring laboratory results, chain-of-custody receipts to show safe disposal of hazardous waste, incident reports from the environmental register, etc.

(g) Should modifications to this document be required, these must be agreed to by all parties concerned.

The Client The Client – the client is responsible for employing the ECO, Contractor and any Sub-contractors for the lifecycle of the facility. It is the client responsibility to ensure that all appointed parties fulfil their obligations in terms of this EMP, i.e. the implementation of this EMP is the Client’s responsibility, and the Client must ensure that all activities taking place on the site are conducted in an environmentally responsible manner and in accordance with the requirements of this EMP. Council Representative The Council Representative will be an appropriately qualified environmental officer of the local municipality. This representative will monitor compliance of this EMP by the client through the ECO. 5.2. Documentation and Record Keeping (a) List of onsite documentation

An environmental register must be kept at the site, which must include the following:

An accident and incident register;

Complaints register;

Emergency Response Plan

Site evacuation plan/maps; and

Method statements

In addition, this EMP, the Emergency Response Plan, as well as the Waste Licence must be kept at the site. The right of the public to information shall be respected in accordance with relevant legislation.

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- 22 - (b) Environmental Register The environmental register should be used to record any relevant daily information related to the operations and current status of the site, including the following information:

Details of audits and inspections carried out by the ECO and/or as detailed in this EMP and follow-ups

Instances of non-conformances found in the EMP, the date of their occurrence, date of corrective action, and date of completion of preventive action

Details of chain of custody documentation

Any other relevant/pertinent daily events

The environmental register should also contain the accident and incident register and/or the complaints register.

(c) Accident and Incident Register An accident and incident register must be kept and should include the following information:

Time, date and place of the accident and/or incident

Who and what was involved

A detailed description of the accident or incident.

(d) Complaints register

A complaints register must be kept for the recording of all complaints lodged regarding the proposed biodigester plant. It is important that the complainant feels that their concerns have been listened to and that appropriate action (within reason) has been taken to address these. The complaints register must include: Detail of the complaint in clear, well-structured language Time and date of complaint and details of complainant for follow-up purposes. Name of the person who received the complaint. Description of action that was taken to address the complaint, including date and time of action. (e) Method statements Method Statements (a template for these purposes is appended to this EMP) will be required for activities that may result in significant impacts according to the ECO. These must address the following aspects:

What – a brief description of the work to be undertaken

How – a detailed description of the process of work, methods and materials

Where – a description of the location of the work (if applicable)

When – the sequencing of actions with commencement and completion date estimates

All Method Statements (MS) must be in place at least 5 working days prior to the relevant construction activities taking place and must be approved by the ECO prior to being implemented. The following MS must as a minimum be made available to address the following decommissioning related impacts:

Stormwater Management

Fire Risk Management

Waste Management

5.3. Environmental Awareness and Training a) For the construction phase, the ECO should conduct on-going Basic Environmental Awareness Training

sessions with the Contractor, his staff and subcontractors prior to any work taking place. The Contractors are required to provide a facility and interpreter (if required).

b) For day to day operations at the site, it is the responsibility of the Client to ensure that all employees and sub-contractors are fully aware of the operational procedures that must be followed in order to minimise health, safety and environmental risks associated with operations at the facility.

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- 23 - 5.4. Matters Pertaining to Non-Conformance onsite

“Non-conformances” would occur when there are deviations from any of the requirements of this EMP. This may also include non-compliance with the relevant environmental regulations. During the construction phase, the Contractor is responsible for reporting non-conformance with the EMP, to the ECO. The Client and the Contractor, in consultation with the ECO must, thereafter, undertake the following activities:

Investigate and identify the cause of non-conformance;

Implement suitable corrective action (appropriate to the magnitude of the environmental impact), as well as prevent recurrence of the problem, with responsibilities assigned for both.

Non-conformances and corrective action must be recorded in the environmental register, and included in the audit reports compiled by the ECO. The Client may introduce some form of penalty system for contractors onsite if compliance with the EMP proves problematic. During the operational phase, it is the Client’s responsibility to appoint an independent ECO to audit the site once every two years. The audit report must be submitted to the DEA&DP, the DEA, Water Affairs and Rustenburg Local Municipality and must include any incidences of non-conformance and recommendations for any corrective action required. In addition, the Client, their contractors, sub-contractors and employees are legally bound by Section 24(h) National Environmental Management Second Amendment Act, Act No. 107 of 1998, which states that it is “an offence for any person to contravene conditions applicable to any environmental authorization granted for a listed activity. A person convicted of an offence is liable to a fine not exceeding R5 million or to imprisonment for a period not exceeding ten years, or to both such fine and such imprisonment” This Environmental Management Programme, when approved, constitutes a Condition applicable to an Environmental Authorisation (or Waste Licence) and any transgression would thus trigger Section 24(h) of the above-mentioned Act. The exact penalty and fines will be decided on, subsequent to consultation with DEA&DP and the local municipality. All staff working on-site must be made aware of the consequences of non-conformance.

A J SILLITO Pr. Sci. Nat., CEAPSA

I:\jobs\SEC Jobs\0151011\May 2017 WLA manure\Outputs\EMP\0151011 RCL Worcester EMP for DBAR Nov 2017.docx

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EMP ANNEXURE A GLOSSARY

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TERMS USED IN THIS EMP The terms used include the following: The term ‘client’ means the owner of the facility to which this EMP applies. The term ‘construction’ means all organised activities concerned with demolition, building, landscaping, maintenance, civil engineering, process engineering, heavy engineering and mining. The term ‘contractor’ means an organisation that contracts with the applicant to carry out the work under a contract, including construction and other services. The term ‘decommission’ means all organised activities concerned with demolition of infrastructure (above and below ground) on site as well as the associated removal of infrastructure on site as well as the rehabilitation and/or site clean up after infrastructure has been removed. The term ‘design’ means the process (and product) of converting a brief into design details ready for documentation, including concept design and design development, and then documentation or detailing of the technical and other requirements for the project in a written form that details the project product sufficiently for it to be constructed or otherwise provided. The term ‘environmental opportunity’ means a potential for beneficial environmental impacts (such as an improvement in air or water quality through environmentally friendly technology alternatives). The term ‘environmental risk’ means a potential for adverse environmental impacts (such as pollution of a water source during decommissioning activities). The term ‘management’ means the planning and interactive controlling of human and material resources to achieve time, cost, quality, performance, functional and scope requirements. It involves the anticipation of changes due to changing circumstances and the making of other changes to minimise adverse effects. The term ‘procurement’ means the collection of activities performed by and for an agency to acquire services and products, including assets, beginning with the identification/detailing of service requirements and concluding with the acceptance (and where applicable, disposal) of the services and products. The term ‘project’ means an undertaking with a defined beginning and objective by which completion is identified. Project delivery may be completed using one contract or a number of contracts. The term ‘service provider’ means a contractor, subcontractor, supplier, consultant (including an agency) and sub-consultant (contracting with a consultant), and their service providers, that contract with a customer to carry out construction, decommissioning, provide other products (including goods) and/or provide services. The term ‘subcontractor’ means an organisation that contracts with a contractor as the customer to carry out construction and related services, and/or provide other products.

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The term ‘supplier’ means an organisation that contracts with a contractor or Principal

Agent to supply a product and/or service.

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EMPR ANNEXURE B POSSIBLE METHOD STATEMENT

TEMPLATE

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METHOD STATEMENT FOR THE:

……………………………………………………. This method statement is to be completed by the Contractor (in consultation with the ECO) at least 5 working days prior to the proposed commencement date of the said work and represents a binding agreement to the Method Statement by all site Contractors and Subcontractors involved in the work for which the Method Statement is submitted. DATE OF SUBMISSION:………………….

CONTRACTOR:…………………….

SUBCONTRACTORS (IF RELEVANT):………………………………………………

A) Describe in detail what work is to be undertaken?

B) Describe in detail where on the site the works are to be undertaken and the extent? Provide sketch plan and grid block reference.

C) When will the works start and what is the anticipated finishing date of these works?

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D) How are the works to be undertaken?

1) Lead supervisor/ foreman name and contact details: 2) Number of personnel:

3) Construction activities:

4) Plant and machinery to be used:

5) Materials to be stored (specify hazardous materials):

6) Other:

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E) What environmental impacts are anticipated and what precautions are proposed to prevent these impacts? (refer to the relevant sections of the EMP for guidance and provide a general camp layout)

Camp site demarcation:

Toilet facilities:

Litter:

Security:

Plant/machinery (operation, servicing, management, storage, refuelling etc.):

Emergencies and fire:

Hazardous materials (handling, management, storage etc.):

Have all personnel involved been through an environmental induction course?

Petrochemical spill remediation and containment measures:

Other:

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DECLARATIONS BY PARTIES 1) CONTRACTOR

I UNDERSTAND THE CONTENTS OF THE METHOD STATEMENT AND THE SCOPE OF THE WORKS

REQUIRED OF ME. I FURTHER UNDERSTAND THAT THE METHOD STATEMENT MAY BE AMENDED

ON APPLICATION TO THE ABOVE SIGNATORIES, AND THAT THE ENVIRONMENTAL CONTROL

OFFICER WILL AUDIT MY COMPLIANCE WITH THE CONTENTS OF THIS METHOD STATEMENT. (PRINT NAME) (SIGNED) DATED:

2) ENVIRONMENTAL CONTROL OFFICER (ECO) THE WORK DESCRIBED IN THIS METHOD STATEMENT, IF CARRIED OUT ACCORDING TO THE

METHODOLOGY DESCRIBED, IS SATISFACTORILY MITIGATED TO PREVENT AVOIDABLE

ENVIRONMENTAL HARM. (PRINT NAME) (SIGNED) DATED: 3) PRINCIPAL AGENT

THE WORK DESCRIBED IN THIS METHOD STATEMENT, IF CARRIED OUT ACCORDING TO THE

METHODOLOGY DESCRIBED, IS SATISFACTORILY MITIGATED TO PREVENT AVOIDABLE

ENVIRONMENTAL HARM. (PRINT NAME) (SIGNED) DATED:

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EMPR ANNEXURE C ROLE OF THE ECO

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DUTIES OF THE ECO 1. Ensuring that the EMP conditions are adhered to at all times and taking action where

the specifications are not being followed.

2. Ensuring that environmental impacts are kept to a minimum.

3. Reviewing and approving method statements in consultation with the Principal Agent.

4. Advising the contractor on environmental issues and assisting in developing

environmentally responsible solutions to problems.

5. Reporting to the applicant on a regular basis and advising of any environmental

impacts.

6. Attending site meetings (when necessary) and giving a report back on the

environmental issues at these meetings and other meetings that may be called

regarding environmental matters.

7. Inspecting and auditing the site and surrounding areas regularly.

8. Establishing and monitoring an on-going environmental awareness program in

conjunction with the contractor.

9. Requesting the removal of person(s) and/or equipment not complying with the

specifications.

10. Keeping both a written and photographic record of progress on site from an

environmental perspective, and an ad hoc record of all incidents or events on site with

environmental ramifications. These records should be dated and accurately

catalogued in the onsite logbook, and separate audit reports.

11. Undertaking continual internal review of the EMP and submitting a report at the end of

the project.

12. The ECO will submit all written instructions and verbal requests to the contractor via

the Municipality project manager.

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EMPR ANNEXURE D

1) SITE LAYOUT PLAN

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EMPR ANNEXURE E

INCIDENT REGISTER & BASIC ACCIDENT REGISTER TEMPLATES

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INCIDENT REGISTER (EXAMPLE)

“Incident” means - an unexpected sudden occurrence, including a major emission, fire or explosion leading to serious danger to the public or potentially

serious pollution of or detriment to the environment, whether immediate or delayed

Date

(yyyy/mm/dd)

Incident

Comments (Include any possible explanations for current

condition and possible responsible parties. Include

photographs, records etc. if available)

Corrective Action Taken (Give details and attach documentation as far

as possible)

Reference no. for

On-Site Logbook (e.g. Rv 6/12 Inc 1)

Signature

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BASIC ACCIDENT REGISTER (EXAMPLE)

Date

(yyyy/mm/dd)

Accident

Names of Persons

Involved

Comments, Including Injuries

Sustained (Include any possible explanations for

current accident. Include photographs,

records etc. if available)

Corrective Action

Taken

(Give details and attach

documentation as far as

possible)

Reference no. for OHS

Documentation and

Attachments (e.g. Rv 6/12 Acc 1)

Signature

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EMPR ANNEXURE F

EAP CURRICULUM VITAE’S

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CV: ADRIAN SILLITO

SPECIALISATION : Environmental Management

NATIONALITY : RSA Citizen

PROFESSIONAL QUALIFICATIONS

: MSc Engineering Geology, Natal University 1991 BSc (Hons) Geology, Sheffield University, 1983

DATE OF BIRTH : 24 November 1961 PROFESSIONAL MEMBERSHIP

: Professional Natural Scientist (Pr.Sci.Nat), Certified Environmental Assessment Practitioner of South Africa (CEAPSA), Member of the International Association for Impact Assessment (MIAIA). Fellow of the Geological Society, London (FGS). Member of the SA Institute of Engineering and Environmental Geologists (SAIEG), Member of the Association of Engineering Geologists (MAEG).

PROFESSIONAL EXPERIENCE From 1/11/01 to date Sillito Environmental Consulting (SEC) Subsoil and groundwater contamination investigation, risk

assessment, analysis, reporting and remedial recommendations. Design, implementation and monitoring of remediation systems. Several thousand projects of this nature have been supervised, project managed and reported on. This includes long term site monitoring, data interpretation and reporting

Liaison and reporting to regulatory authorities with regard to contamination issues

Phase 1 & 2 Environmental Due Diligence & Waste Audits for various national and international companies

Production of generic environmental audit protocols

Environmental Impact Assessments for a wide range of proposed activities including residential, commercial, industrial, petrochemical, chemical and telecommunications. This involved the compilation, editing and review of all documents

Site specific environmental management programmes and on-site support/ECO services. Including the review of final documents.

Professional review of reports submitted to the Department of the Environment for the Minister of Environmental Affairs and Development Planning

Green Star SA training, project management and coordination

1996 to 10/2001 K & T Consulting Engineers Contamination Investigation and Risk Assessment

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Contamination investigation, risk assessment and remediation proposals and systems design for a large number of petrochemical facilities countrywide

Geotechnical Investigation Geotechnical investigations for a wide variety of structures, from

pipeline route investigations, large-scale site evaluation for housing, both low and high cost, to individual structures from single houses to multi storey hotels

Slope stability analysis, stabilisation proposals and project management

Quarry site location, materials analysis and reporting

Project Management Project management of the engineering design to closure of

Faure landfill site. Project involved geophysical and geohydrological, hydrological and geotechnical assessment as well as the engineering design for the capping layer

Environmental Impact Assessment Environmental Impact Assessments within the petrochemical,

chemical, mining and quarrying environments, projects completed in all 9 provinces

Development of Environmental Management Plans

Environmental Control Officer experience on various projects

Environmental Management Programme Reporting (Quarry sites)

Review of applications for authorisation (in terms of the Environment Conservation Act) on behalf of the Department of Environment, DEA&DP (Western Cape)

General environmental advice to DEA&DP with regard to the policy development for the Western Cape

Environmental Management Systems ISO 14001 Environmental Management Systems training with

Casella International, UK, 2000 Implementation of ISO 14001 environmental management

systems EARA approved Environmental Auditor course (March 2001)

Phase 1 Environmental Audits (Merger & Acquisition Audits) individually and in conjunction with international environmental companies

1994 – 1996 Africon Geotechnical & Materials Waste disposal site conceptual design (including costing) for

DWAF permit application. Location of suitable liner materials Geotechnical investigation and foundation/support design for a

wide variety of projects from tunnels, township establishment, townhouses, bridges, underpasses, receiver masts, law court complexes, hotels to warehouse developments

Orange-Vaal canal project, route analysis with API (Aerial

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Photograph Interpretation), on-site investigation and construction recommendations. Gariep to Springfontein pipeline investigation

Underground mine backfilling investigation for surface stabilisation of sewage works, analysis and proposal of remedial measures

1992 - 1994 Lesotho Highlands Project Contractors Responsible for all geological and geotechnical input at the Katse

Intake site from slope stability analysis to predicting geological problem areas (stress, lineation intersection, quarry materials quality)

Tunnel support recommendations and classification of ground conditions

Aggregate quarry quality control and mining methodology including environmental controls in terms of waste discharges

1990 - 1991 Natal University, Durban: MSc Engineering Geology One year’s full time lecture course including the soil mechanics

component which was provided by the Civil Engineering Department

Thesis: Analysis of six co-disposal landfill sites in KwaZulu Natal

1988 - 1990 George Orr & Associates Lower Fish River Government water scheme: Site Eng. Geologist.

Dam foundation analysis, grout curtain recommendations, tunnel feasibility investigations (drilling investigations), mapping, quarry monitoring and environmental controls

Ladysmith Flood Attenuation Scheme: Dam site location, investigation and quarry location and evaluation

Henties Bay aquifer recharge project, dam site location and evaluation via satellite imagery and targeted drilling

1984 – 1988 Mining & Exploration Field Exploration Geologist, open cast coal operations

Opencast coal site geologist, quality control on site and at the processing plant, including mine planning

Exploration/Shaft Geologist gold mining environment. Quality control, reserve determination and drilling exploration

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CV: COLLEEN McCREADIE

SPECIALISATION : Environmental Management

NATIONALITY : South African

PROFESSIONAL QUALIFICATIONS : BA Political Studies and Economics, UCT, 1997 BComm (Hons) Economics, UCT, 2000

DATE OF BIRTH : 25 June 1976 PROFESSIONAL MEMBERSHIP : Member of the International Association for Impact Assessment

(IAIA). Member of the National Association for Clean Air (NACA) Associate Member of the Institute for Waste Management of Southern Africa (IWMSA)

COURSES AND SEMINARS ATTENDED

: Sustainable Development and Environmental Analysis and Development Planning Modules towards a BPhil in Sustainable Development Planning and Management, Sustainability Institute, University of Stellenbosch, 2009 Workshop on Basic Assessment, DEA&DP, 2007 Ten Years of EIA in South Africa, DEAT, 2008 Waste Act Roadshow, DEA, 2009 Workshop on the Waste Act, DEA&DP, 2010 Workshop on the 2010 EIA Regulations, DEA&DP, 2010 Workshop on the 2010 EIA Regulations, DEA&DP, 2011 IAIAsa National Conference, 2012 IWMSA Waste Conference, 2014 Workshop on the 2014 EIA Regulations, DEA&DP, 2015 Workshop: In-Stack Emission Monitoring and Reporting in Compliance with Atmospheric Emission Licence Requirements, NACA, 2015 Workshop: Challenges of Dust Deposition Monitoring, NACA, 2015 Presentation by SEC: Maintaining Compliance with AEL Conditions, NACA, 2016 Workshop on 21 (i) & (c) Water Uses presented by the DWS, 2017

PROFESSIONAL EXPERIENCE From 01/03/12 to date SEC Environmental Impact Assessments (project management; report

compilation; compliance monitoring and auditing; public participation management; legislation and regulation review)

EIA’s, Basic Assessments, Rectification Applications, Licence Applications, Permit Applications, Service Provider Registrations in terms of the NEMA, NEM: Waste Act, NEM: Air Quality Act and local by-laws.

From 01/03/11 to 28/02/12 Freelance Environmental Consultant EIA’s and Basic Assessments undertaken in terms of the NEMA

Work undertaken for KHULA Environmental Consultants; SiVEST Environmental Division (Cape Town) and Sillito Environmental

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Consulting (SEC) From 1/07/07 to 28/02/11 SEC Environmental Impact Assessments

On-site Environmental Control Officer (ECO) work

Environmental authority consultation

Input into Environmental Management Plans for construction and operational phase work

From 08/11/06 to 31/05/07 SRK Consulting Junior level: Environmental Impact Assessments within the

residential development and mining sectors, including retrospective authorisation for illegal activities under the NEMA Section 24G legislation

ECO work

Impumelelo Innovations Award Trust: Independent

Researcher An NGO which awards excellence in public-private partnerships

for pro-poor service delivery. Assessing 21 projects submitted to Impumelelo in 2006, to

identify key issues contributing to their success or failure, and analysing the identified issues to recognise trends across the projects, thereby generalising drivers of success or of failure.

01/02/03 – 01/10/06 ERA Steer False Bay Real estate sales associate for the Noordhoek area

Responsibilities included property valuation, property market trend analysis, the marketing of properties including the design and copy for marketing materials and advertisements, negotiation of sales and maintaining client relationships from first contact to after-sales service.