Adidas Environmental - Guidelines - English PDF
Adidas Environmental - Guidelines - English PDF
Adidas Environmental - Guidelines - English PDF
TABLE OF CONTENTS
PREFACE................................................................................................................................................................ 3
SECTION 1 INTRODUCTION .............................................................................................................................. 4
1.1 WORKPLACE STANDARDS AND GUIDING PRINCIPLES ............................................................................... 4
1.2 ENVIRONMENTAL PERMITS AND LEGAL REQUIREMENTS .......................................................................... 5
1.3 ENVIRONMENTAL MANAGEMENT SYSTEMS .............................................................................................. 6
1.4 SUSTAINABLE RESOURCE USE ................................................................................................................ 6
1.5 EMISSIONS TO WATER AND AIR, WASTE .................................................................................................. 7
1.6 RISKS AND HAZARDS .............................................................................................................................. 7
1.7 FURTHER GUIDANCE .............................................................................................................................. 8
SECTION 2 ENVIRONMENTAL MANAGEMENT SYSTEMS ............................................................................ 9
2.1 ENVIRONMENTAL MANAGEMENT SYSTEM ELEMENTS ............................................................................... 9
2.2 MEASUREMENT AND REPORTING .......................................................................................................... 10
SECTION 3 SUSTAINABLE RESOURCE USE................................................................................................. 11
3.1 ENERGY EFFICIENCY ............................................................................................................................. 11
3.1.1 Energy Management Programmes .................................................................................................. 11
3.1.2 Energy Efficiency ............................................................................................................................... 11
3.1.3 Green Buildings ................................................................................................................................. 12
3.2 CLIMATE CHANGE AND REDUCING GREENHOUSE GASES (GHGS)........................................................... 13
3.2.1 Carbon Footprint ............................................................................................................................... 13
3.3 WATER CONSERVATION AND ACCESS TO WATER .................................................................................... 14
3.3.1 Water Monitoring and Management................................................................................................. 14
3.3.2 Process Water Reuse and Recycling................................................................................................ 15
3.3.3 Building Facility Operations.............................................................................................................. 15
3.3.4 Cooling Systems ................................................................................................................................ 15
3.3.5 Heating Systems................................................................................................................................ 16
3.3.6 Water Use .......................................................................................................................................... 16
3.3.7 Further Guidance............................................................................................................................... 16
SECTION 4 EMISSIONS TO WATER AND AIR, WASTE ................................................................................ 17
4.1 WASTE ................................................................................................................................................. 17
4.1.1 Types of Waste................................................................................................................................... 17
4.1.2 General Waste Management ............................................................................................................ 17
4.1.3 Waste Management Planning ........................................................................................................... 17
4.1.4 Waste Prevention............................................................................................................................... 18
4.1.5 Recycling and Reuse ......................................................................................................................... 18
4.1.6 Treatment and Disposal.................................................................................................................... 18
4.1.7 Hazardous Waste Management........................................................................................................ 19
4.1.8 Waste Storage.................................................................................................................................... 19
4.1.9 Transportation ................................................................................................................................... 19
4.1.10 Monitoring........................................................................................................................................ 19
4.2 WASTEWATER DISCHARGE .................................................................................................................... 20
4.2.1 Discharge of Wastewater .................................................................................................................. 20
4.2.2 Wastewater Management ................................................................................................................. 21
4.2.3 Industrial Wastewater ....................................................................................................................... 21
4.2.4 Stormwater Management ................................................................................................................. 22
4.2.5 Sanitary Wastewater ......................................................................................................................... 22
4.2.6 Wastewater Treatment and Discharge Standards .......................................................................... 22
4.2.7 Emissions from Wastewater Treatment Operations ....................................................................... 23
Preface
In order to promote uniform standards in environmental management, the adidas Group has
developed tools to measure and assess the environmental performance and risks at factories doing
business with us. These Guidelines are based on international industry practice and standards for
environmental management and sustainable resource consumption.
The Guidelines detail requirements which will allow suppliers to comply with the adidas Groups
Workplace Standards and also support the adidas Groups ongoing development of policies and
strategies to address environmental sustainability along our supply chain. The guidelines described
here do not necessarily reflect the national laws of all the countries where suppliers are based, and it
is the responsibility of the individual suppliers to ensure that they meet all legal requirements and
obtain the necessary approvals, permissions and consents related to the environmental impact of
their operations.
These Guidelines are minimum requirements only. They are not industry specific and in some cases
suppliers may be required to achieve higher standards depending on the nature of the industrial
processes or manufacturing activities undertaken on site.
Please consult with SEAs designated environmental experts before making any major investments in
the construction or reengineering of systems.
Section 1 Introduction
The adidas Group Environmental Guidelines have been prepared as a technical reference for our
business partners and in particular those involved in manufacturing activities. The Guidelines draw on
good industry practice and describe ways to prevent pollution, manage and control environmental
impacts and avoid the depletion of natural resources. The performance levels and measures that are
set out in these Guidelines are generally achievable using existing technologies, at an affordable cost.
In applying these Guidelines, adidas Group business partners must:
Understand their obligation under the adidas Groups Workplace Standards.
Acknowledge and be aligned with the guiding principles set out in Section 1.2 below.
Comply with all relevant requirements and standards as stated in the Guidelines. When
country-specific regulations differ from the levels and measures in the Guidelines, meet
whichever is the more stringent.
Recognise and take action with respect to the specific hazards and risks associated with
facility operations and processes.
Establish site-specific targets for improvement, with an appropriate timetable for achieving
them.
These Guidelines complement, and should be read alongside, the adidas Groups Health & Safety
Guidelines 2010 and the adidas Groups Environmental Best Practices Guidelines 2005.
These are the core values found in sport. Sport is the soul of the adidas Group. We measure
ourselves by these values, and we measure our business partners in the same way.
Consistent with these values, we expect our partners contractors, subcontractors, suppliers, and
others to conduct themselves with the utmost fairness, honesty and responsibility in all aspects
of their business.
We use the adidas Group Workplace Standards as a tool to assist us in selecting and retaining
business partners who follow business practices consistent with our policies and values. As a set
of guiding principles, the Workplace Standards also help identify potential problems so that we can
work with our business partners to address issues of concern as they arise. Business partners will
develop and implement action plans for continuous improvement in factory working conditions.
Progress against these plans will be monitored by the business partners themselves, our internal
monitoring team and external independent monitors.
Specifically, we expect our business partners to operate work places where the following
standards and practices are implemented: []
Environmental Requirements
Business partners must make progressive improvement in environmental performance in their
own operations and require the same of their partners, suppliers and subcontractors. This
includes: integrating principles of sustainability into business decisions; responsible use of natural
resources; adoption of cleaner production and pollution prevention measures; and designing and
developing products, materials and technologies according to the principles of sustainability.
The adidas Groups Workplace Standards include specific Environmental Requirements (see insert
above). To support these requirements, the adidas Group expects our business partners to commit to
a set of guiding principles that require them to:
Meet or exceed legal requirements.
Take a precautionary approach to environmental, health and safety challenges.
Adopt a holistic approach to handle all environmental, health and safety issues as relevant for
their operations.
Continuously develop strategies to reduce consumption of resources, prevent pollution and
improve the overall environmental impact from their own operations and those of their
suppliers, service providers and subcontractors.
Continuously develop programmes and objectives, based on results in the areas, both
qualitatively and quantitatively measured via indicators and key performance indicators.
Continuously seek ways to improve the work environment to reduce risks that can cause
accidents and pollution. This requires the adoption of a risk management perspective and
continuously reducing the production related risks regarding accidents, chemicals and toxic
substances, including potential future contamination.
Adopt and implement certifiable environmental management systems where production
processes have the potential for significant environmental impact.
The adidas Group expects our suppliers and partners to develop strategies, set objectives and in
general drive improvement in the following but not limited to environmental areas:
Climate change, energy consumption and greenhouse gas emissions
Emissions to water and air, waste, noise
Materials and use of resources
Risks and hazards, including chemicals.
It is our overall ambition that our suppliers and partners continuously improve and reduce their
overall environmental, health and safety impact.
The adidas Group respects the laws and regulations in the countries in which it operates and requires
that its suppliers and partners do the same. For a business to be effective in managing its
environmental risks and liabilities it must be compliant with the law. A well run business will meet or
exceed regulatory requirements, track legislative changes and obtain and maintain all necessary
permits and approvals. Permits and approvals may include, but are not limited to:
Business licenses
Environmental impact assessments and land use consents for the nature of the operations
and processes on site
Construction and building permits
Surface and groundwater abstraction licenses
Permits for the discharge of wastewater, emission of air pollutants and disposal of hazardous
and non-hazardous waste
Operating permits for boilers, pressurised vessels, and for mechanical, electrical or chemical
processes, where required
Operating licenses for treatment plants and processes and for their operators
Licenses for the storage and handling of hazardous chemicals or flammable substances
Permits for the decommissioning of plant and contaminated soil clean-up and remediation
Handling and disposal of asbestos.
Should any requirement stated in these Environmental Guidelines violate or conflict with the
applicable local law, the law takes precedence.
The adidas Groups business partners are required to adopt or establish a suitable environmental
management system whose scope is related to the content of these Guidelines.
The adidas Group promotes the adoption of lean manufacturing and we encourage our suppliers and
partners to minimise their use of materials and other resources in production processes. Such
resources could be, but are not limited to, energy, water, air, chemicals and raw materials. All
materials that can be reused or recycled should be reused or recycled.
For further guidance, please refer to the following sections in this document:
Energy efficiency (Section 3.1)
Water conservation and access to water (Section 3.3)
Materials efficiency (see Section 4.1, Waste Management)
The adidas Group expects our business partners to progressively reduce factors that cause pollution,
to assess the impacts of their manufacturing processes and to identify and act on the potential for
improvement. Moreover, suppliers and partners should:
Monitor and treat all effluents as required by law
Manage waste systematically, with due care
Monitor and manage noise both as an environmental issue and as a health and safety
concern.
For further guidance, please refer to the following sections in this document:
Waste (Section 4.1)
Wastewater discharge (Section 4.2)
Air emissions (Section 4.3)
Noise (Section 4.4. See also adidas Group Health & Safety Guidelines 2010)
Soil and groundwater contamination (Section 4.5).
To control pollution and effectively manage environmental issues, our partners must include
environmental considerations into their day-to-day business operations in an organised, hierarchical
approach that includes:
Identifying environmental hazards and associated risks as early as possible in facility
development, including the incorporation of environmental considerations into the site
selection process, building design, product development, engineering planning, or layout and
process change plans.
Engaging technical experts and professionals who have the experience, competence, and
training necessary to assess and manage environmental impacts and risks and carry out
specialised environmental management functions.
Understanding the likelihood and magnitude of environmental risks, based on:
o The nature of the manufacturing activities, such as whether the production processes will
generate significant quantities of emissions or effluents, or involve hazardous materials
or processes.
o The potential consequences to workers, communities or the environment if hazards are
not adequately managed.
Developing suitable environmental management plans and systems, as described below.
The adidas Group expects our business partners to adopt a risk management approach in their
handling of operational risks, hazards and chemicals. The adidas Group requires our partners to
conduct regular risk assessments and to seek to continuously minimise risks and hazards. Moreover,
the adidas Group requires our suppliers to have strict management systems in place for storage,
handling and use of chemicals, including chemical risk assessments and the proper training of
personnel in handling chemicals.
The adidas Groups Environmental Guidelines draw extensively from the guidance contained in the
International Finance Corporation (IFC) and World Bank Environmental Health and Safety (EHS)
Guidelines 1997, which have been revised, updated and added to, to reflect our specific requirements.
For more industry-specific information on EHS issues, please see the complete list of industry-sector
guidelines published by the IFC at:
www.ifc.org/ifcext/enviro.nsf/Content/EnvironmentalGuidelines.
As outlined in Section 1.3, the adidas Group expects our suppliers to implement environmental
management systems (EMS) that are appropriate to the size and environmental impact of their
operations.
This ongoing process enables the organisation to continually improve its EMS and its overall
environmental performance. It should be emphasised that the EMS does not produce results
automatically. It will do so only if the corresponding objectives are defined and programmes
implemented. The adidas Group strongly supports a results-driven and improvement-focussed
approach. The system is only valuable if substantial environmental improvements are achieved with
the help of the system. The system is the vehicle to achieve these results.
In addition to improved environmental performance within all business processes, the potential
benefits associated with an effective EMS include:
Assuring customers of commitment to effective environmental management
Maintaining good public/community relations
Satisfying investor criteria and improving access to capital
Obtaining insurance at reasonable cost
Enhancing image and market share
Improving cost control
Conserving input materials and energy
Fostering development and sharing of solutions to environmental problems.
Certified Systems
Any partner whose operations and facilities are of sufficient scale or contain processes that present
significant hazards and risks to the environment is expected to establish a formal environmental
management system, such as ISO 14001, or Europes Eco-Management and Audit Scheme (EMAS).
The system needs to be certified by a reputable certification body. The adidas Group reserves the right
to disqualify any certification body that has not proven itself to operate with integrity and
independence in the granting and renewal of ISO 14001 or EMAS certification.
To ensure that a systematic improvement programme can be put in place and evaluated, all suppliers
are requested to monitor and report on their performance. All permits, legal limits, but also standard
indicators, such as energy and water consumption, must be monitored on a regular basis,
summarised and held ready for reporting to the adidas Group.
An example of the type of data that should be collected and reported is given in Appendix 1.
The adidas Group supports the sustainable use of materials and the conservation of natural
resources. We recognise that uncontrolled consumption of resources may have dire implications for
local communities and for the planet. We are therefore committed to act wherever we have direct
influence in the design of our products and in the selection of materials and where we see
measurable adverse impacts from the manufacture and transportation of our goods. We expect our
suppliers and business partners to be aligned with globally agreed policies and frameworks for
sustainable resource use and have a strategy in place for a stepwise improvement in their efficiency,
with specific measures to eliminate all forms of waste (as described in Section 4.1) and to reduce
their:
Energy consumption, with a primary focus on energy efficiency
Carbon emissions and associated impacts on greenhouse gases (GHG)
Water footprint, with a focus on water conservation and recycling efforts.
Buildings today account for over 40% of the worlds energy use. Manufacturing facilities also consume
energy in process heating and cooling; process and auxiliary systems, such as motors, pumps, and
fans; compressed air systems and heating, ventilation and air conditioning systems (HVAC); lighting
systems. Energy management at the facility level should be viewed in the context of overall
consumption patterns, including those associated with production processes and supporting utilities,
as well as overall impacts associated with emissions from power sources.
For any energy-using system, a systematic analysis of energy efficiency improvements and cost
reduction opportunities should include a hierarchical examination of opportunities to:
Demand/Load Side Management by reducing loads on the energy system, and
Supply Side Management by:
o Reducing losses in energy distribution
o Improving energy conversion efficiency
o Exploiting energy purchasing opportunities
o Using lower-carbon fuels.
Green buildings refer to the use of environmentally preferable practices and materials in the design,
location, construction, operation, and disposal of buildings. It applies to both renovation and
retrofitting of existing buildings and construction of new buildings. Many countries have developed
their own standards for green buildings, examples include:
Germany: The German Association for Sustainable Building (DGNB) has developed a quality
certification for buildings with five sustainability criteria. See www.dgnb.de
Japan has developed the so-called Comprehensive Assessment System for Building
Environmental Efficiency (CASBEE). See http://www.ibec.or.jp/CASBEE/english/index.htm
United Kingdom: The British Research Establishment Environmental Assessment Methodology
(BREEAM) is the most widely used international method for assessing building quality and
performance in terms of energy, environmental impact and health indicators. See
http://www.breeam.org/ and http://www.thegreenguide.org.uk/
USA: The Leadership in Energy and Environmental Design (LEED) Green Building Rating
System, developed by the US Green Building Council (USGBC), provides a suite of standards
for environmentally sustainable construction. See http://www.usgbc.org/
In designing and constructing new buildings, business partners are strongly encouraged to adopt
green building practices, following the guidance given above. Certification against a specific standard
is, however, optional.
Industrial facilities and processes have the potential to contribute to global warming through the
emissions of greenhouse gases (GHGs). Of most concern are emissions of what are known as long-
lived greenhouse gases, the most important of which are CO2, methane, nitrous oxide and CFC
gases1. In total they account for more than 97% of the direct effect of the long-lived gases on how
much heat is retained in the atmosphere. A decade ago countries came together to sign an
international treaty the 1994 United Nations Framework Convention on Climate Change to reduce
the impact of greenhouse gases, and through the supplementary and binding Kyoto Protocol reduction
targets were set2. The Kyoto Protocol expires in 2012 and a new round of targets and agreements will
be established by the United Nations in 2011. These will increase the pressure on industry globally to
reduce greenhouse gases and in particular carbon emissions from fossil fuels. Sustained reduction in
GHGs is essential if global warming is to be held below the 2 degree threshold that has been
recommended by the Intergovernmental Panel on Climate Change (IPCC)3.
For manufacturing operations, greenhouse gases may be generated from direct emissions from
facilities within the physical boundary of the site and from indirect emissions associated with the off-
site production of power used by those facilities. Recommendations for the reduction and control of
greenhouse gases include:
Enhancement of energy efficiency (as described earlier)
Protection and enhancement of sinks and reservoirs of greenhouse gases, e.g. through
reforestation
Development and use of renewable forms of energy, both on-site and as an off-site energy
source.
Carbon footprint is a term used to describe the amount of GHG emissions caused by a particular
activity or facility, and therefore a way for businesses to assess their contribution to climate change.
Understanding GHG emissions and where they come from is necessary in order to reduce them. In the
past, consumer goods companies wanting to measure their carbon footprints have focussed on their
own emissions, but now increasing attention is given to emissions along the entire value chain: from
raw material to production, distribution and retail of the product, through to its final disposal by the
consumer.
Supply chain GHG emissions, which include those associated with processes not controlled by the
adidas Group directly, can be measured at either the supplier level or the level of an individual
product. The adidas Group encourages business partners to begin to map their own carbon footprints
in order to reduce GHG emissions and to identify cost saving opportunities through energy reduction
programmes.
1
The six greenhouse gases that form part of the Kyoto Protocol to the United Nations Framework Convention on
Climate Change include carbon dioxide (C02); methane (CH4); nitrous oxide (N2O); hydrofluorocarbons (HFCs);
perfluorocarbons (PFCs); and sulfur hexafluoride (SF6).
2
The Kyoto Protocol, an international and legally binding agreement to reduce greenhouse gas emissions
worldwide, entered into force on February 16, 2005.
3
See Climate Change 2007 Fourth IPPC Assessment Report
More complete guidance on how to conduct a carbon footprinting exercise can be found in:
The Greenhouse Gas Protocol, A Corporate Accounting and Reporting Standard, and Project
Accounting Protocol and Guidelines: http://www.ghgprotocol.org/standards
ISO 14040-14044 Environmental Management -- Life cycle assessment -- Requirements and
Guidelines, 2006
PAS 2050, standards on measuring the greenhouse gas emissions of products and services,
prepared by BSI British Standards: http://www.bsigroup.com/en/Standards-and-
Publications/How-we-can-help-you/Professional-Standards-Service/PAS-2050/
As a minimum, adidas Group partners must comply with the GHGs reduction and energy efficiency
targets established for their industry in the countries where they operate.
For further guidance on energy management see the adidas Groups Environmental Best Practices
Guide and the IFC Energy Conservation Guidelines.
Water conservation programmes should be implemented in line with the magnitude and cost of water
consumed. These programmes should promote the continuous reduction of water consumption and
achieve savings in the water pumping, treatment and disposal costs. Water conservation measures
may include water monitoring/management techniques; process and cooling/heating water recycling,
reuse, and other techniques; and sanitary water conservation techniques. Where possible, it is
recommended that business partners include:
Storm/rainwater harvesting and use
Zero discharge design/use of treated wastewater to be included in project design processes
Use of localised recirculation systems in plant/facility/shops (as opposed to centralised
recirculation systems), with provision only for make-up water
Use of dry process technologies, e.g. dry quenching
Process water system pressure management
Project design to have measures for adequate water collection, spill control and a leakage
control system.
Water measurement (metering) should emphasise areas of greatest water use. Based on the review of
metering data, unaccounted use indicating major leaks at industrial facilities could be identified.
Opportunities for water savings in industrial processes are highly industry-specific. However, the
following techniques have all been used successfully and should be considered in conjunction with the
development of the metering system described above.
Washing Machines: Many washing machines use large quantities of hot water. Use can
increase as nozzles become enlarged due to repeated cleaning and/or wear.
Monitor machine water use, compare with specifications and replace nozzles when water and
heat use reaches levels warranting such work.
Water reuse: Common water reuse applications include countercurrent rinsing, for example
in multi-stage washing and rinsing processes, or reusing wastewater from one process for
another with less exacting water requirements. Water jets/sprays: If processes use water jets
or sprays (e.g. to keep conveyors clean or to cool product), review the accuracy of the spray
pattern to prevent unnecessary water loss.
Flow control optimisation: Industrial processes sometimes require the use of tanks, which are
refilled to control losses. It is often possible to reduce the rate of water supply to such tanks,
and sometimes to reduce tank levels to reduce spillage. If the process uses water cooling
sprays, it may be possible to reduce flow while maintaining cooling performance. Testing can
determine the optimum balance.
o If hoses are used in cleaning, use flow controls to restrict wasteful water flow.
o Consider the use of high pressure, low volume cleaning systems rather than using large
volumes of water sprayed from hosepipes.
o Using flow timers and limit switches to control water use.
o Using clean-up practices rather than hosing down.
Consumption of building and sanitary water is typically less than that used in industrial processes.
However, savings can readily be identified as outlined below:
Compare daily water use per employee to existing benchmarks taking into consideration the
primary use at the facility, whether sanitary or including other activities such as showering or
catering
Regularly maintain plumbing and identify and repair leaks
Shut off water to unused areas
Install self-closing taps, automatic shut-off valves, spray nozzles, pressure reducing valves
and water conserving fixtures (e.g. low-flow shower heads, faucets, toilets, urinals and
spring-loaded or sensored faucets)
Operate dishwashers and laundries on full loads and only when needed
Install water-saving equipment in lavatories, such as low-flow toilets.
Heating systems based on the circulation of low or medium pressure hot water (which do not
consume water) should be closed. If they do consume water, regular maintenance should be
conducted to check for leaks. However, large quantities of water may be used by steam systems, and
this can be reduced by business partners adopting the following measures:
Repair of steam and condensate leaks and repair of all failed steam traps;
Return of condensate to the boilerhouse and use of heat exchangers (with condensate return)
rather than direct steam injection where process permits
Flash steam recovery
Minimising boiler blowdown consistent with maintaining acceptably low dissolved solids in
boiler water. Use of reverse osmosis boiler feed water treatment substantially reduces the
need for boiler blowdown
Minimising deaerator heating.
For further guidance on water saving techniques please refer to the adidas Groups Environmental
Best Practices Guidelines 2005.
Waste is any solid, liquid, or contained gaseous material that is being discarded by disposal, recycling,
burning or incineration. Specific types of waste are described below. Manufacturing facilities that
generate and store wastes should adopt the following practices:
Establish waste management priorities at the outset of activities, based on an understanding
of potential Environmental, Health, and Safety (EHS) risks and impacts and considering waste
generation and its consequences.
Establish a waste management hierarchy that considers prevention, reduction, reuse,
recovery, recycling, removal and finally disposal of wastes.
Avoid or minimise the generation of waste materials, as far as practicable.
Where waste generation cannot be avoided, it should be minimised, recovered and/or reused.
Where waste cannot be recovered or reused, it should be treated, destroyed and disposed of
in an environmentally sound manner.
4.1 Waste
Manufacturing operations generate many different types of waste, both hazardous and non-
hazardous. This section of the Guidelines considers important concepts in the management and
control of waste, including waste prevention, recycling, reuse, treatment and disposal.
Solid (non-hazardous) wastes generally include any garbage or refuse, such as metal scrap and
residual waste from industrial operations, such as boiler slag or fly ash.
Hazardous waste shares the properties of a hazardous material (e.g. ignitability, corrosivity, reactivity,
or toxicity), or other physical, chemical or biological characteristics that may pose a potential risk to
human health or the environment if improperly managed.
Sludge from a waste treatment plant, water supply treatment plant, or air pollution control facility and
other discarded material from industrial operations needs to be evaluated to establish whether it
constitutes a hazardous or a non-hazardous waste.
Waste management should be handled through a waste management system that addresses issues
linked to waste minimisation, generation, transport, disposal and monitoring, as described below.
Facilities that generate waste should characterise their waste according to composition, source, types
of wastes produced, generation rates, or according to local regulatory requirements. Effective
planning and implementation of waste management strategies should include:
Review of new waste sources during planning, siting, and design activities, including during
equipment modifications and process alterations, to identify expected waste generation,
pollution prevention opportunities, and necessary treatment, storage, and disposal
infrastructure.
Collection of data and information about the process and waste streams in existing facilities,
including characterisation of waste streams by type, quantities and potential use/disposition.
Establishment of priorities based on a risk analysis that takes into account the potential EHS
risks during the waste cycle and the availability of infrastructure to manage the waste in an
environmentally sound manner.
Definition of opportunities for source reduction, as well as reuse and recycling.
Definition of procedures and operational controls for on-site storage.
Definition of options/procedures/operational controls for treatment and final disposal.
Processes should be designed and operated to prevent, or minimise, the quantities of wastes
generated and hazards associated with the wastes generated by:
Substituting raw materials or inputs with less hazardous or toxic materials or with those
where processing generates lower waste volumes.
Applying manufacturing processes that convert materials efficiently, providing higher product
output yields, including modification of design of the production process, operating conditions,
and process controls.
Instituting good housekeeping and operating practices, including inventory control to reduce
the amount of waste resulting from materials that are out-of-date, off-specification,
contaminated, damaged, or excess to plant needs.
Instituting procurement measures that recognise opportunities to return usable materials
such as containers and which prevent the over-ordering of materials.
Minimising hazardous waste generation by implementing stringent waste segregation to
prevent the commingling of non-hazardous and hazardous waste.
In addition to the implementation of waste prevention strategies, the total amount of waste may be
significantly reduced through:
Evaluation of waste production processes and identification of potentially recyclable materials
Identification and recycling of products that can be reintroduced into the manufacturing
process
Investigation of external markets for recycling by other industrial processing operations
Establishing recycling objectives and formal tracking of waste generation and recycling rates
Providing training and incentives to employees in order to meet objectives.
If waste materials are still generated after the implementation of feasible waste prevention, reduction,
reuse, recovery and recycling measures, waste materials should be treated and disposed of and all
measures be taken to avoid potential impacts to human health and the environment.
Selected management approaches should be consistent with the characteristics of waste and local
regulations and may include:
On-site or off-site biological, chemical, or physical treatment of the waste material to render
it non-hazardous prior to final disposal
Treatment or disposal at permitted facilities specially designed to receive the waste.
Disposal of waste should be secured through the use of formal procurement agreements with
qualified waste vendors who have the required permits, certifications and approvals from government.
Hazardous wastes should always be segregated from non-hazardous wastes. If the generation of
hazardous waste cannot be prevented, then management should focus on the prevention of harm to
health, safety and the environment, according to the following principles:
Understanding potential impacts and risks associated with the hazardous waste over its
complete life cycle
Ensuring that contractors handling, treating, and disposing of hazardous waste are reputable
and legitimate enterprises, licensed by the relevant regulatory agencies and following good
international industry practice for the waste being handled
Ensuring compliance with applicable local and international regulations.
It is noted that hazardous waste materials can be generated in relatively small quantities, including
spent solvents and oily rags, empty paint cans, chemical containers, used lubricating oil, used
batteries and lighting equipment. These wastes should also be managed according to the above
principles.
Hazardous waste should be stored so as to prevent or control accidental releases to air, soil and water
resources. As a minimum, suppliers should:
Store waste in a manner that prevents the commingling or contact between incompatible
wastes and allows for inspection between containers to monitor leaks or spills
Store in closed containers away from direct sunlight, wind and rain
Avoid underground storage tanks and underground piping of hazardous waste.
Hazardous waste storage activities should be subject to special management actions, conducted by
employees who have received specific training in handling and storage of hazardous wastes. Also spill
response and emergency plans must be in place to address their accidental release.
4.1.9 Transportation
On-site and off-site transportation of waste should be conducted so as to prevent or minimise spills,
releases and exposures to employees and the public. All waste containers designated for off-site
shipment should be secured and labelled with the contents and associated hazards, be properly
loaded on the transport vehicles before leaving the site and be accompanied by a shipping paper (i.e.
manifest) that describes the load and its associated hazards.
4.1.10 Monitoring
Monitoring activities associated with the management of hazardous and non-hazardous waste should
include regular visual inspections of all waste storage collection and storage areas for evidence of
accidental releases and to verify that wastes are properly labelled and stored.
When significant quantities of hazardous wastes are generated and stored on site, monitoring
activities should include:
Inspection of vessels for leaks, drips or other indications of loss
Identification of cracks, corrosion or damage to tanks, protective equipment or floors
Verification of locks, emergency valves and other safety devices for easy operation
Checking the operability of emergency systems
Documenting results of testing for integrity, emissions or monitoring stations
Documenting any changes to the storage facility, and any significant changes in the quantity of
materials in storage.
Monitoring records for hazardous waste collected, stored or shipped should include:
Name and identification number of the material(s) composing the hazardous waste
Physical state (i.e. solid, liquid, gaseous or a combination of one, or more, of these)
Quantity (e.g. kilograms or litres, number of containers)
Waste shipment tracking documentation to include quantity and type, date dispatched, date
transported and date received, record of originator, recipient and transporter
Method and date of storing, repacking, treating or disposing at the facility, cross-referenced to
specific manifest document numbers applicable to the hazardous waste
Location of each hazardous waste within the facility and the quantity at each location.
Manufacturing operations may generate different types of wastewater, including process wastewater,
sanitary wastewater, wastewater from utility operations and also site run-off or stormwater. This
section of the Guidelines considers the control and treatment of different types of wastewater and the
minimum standards that must be met for its discharge.
Septic Systems
Septic systems are commonly used for treatment and disposal of domestic sanitary sewage in areas
with no sewerage collection networks. Septic systems should only be used for treatment of sanitary
sewage. They are not suitable for industrial wastewater treatment. When septic systems are used,
they should be:
Properly designed and installed in accordance with local regulations and guidance to prevent
any hazard to public health or contamination of land, surface or groundwater
Well maintained to allow effective operation
Installed in areas with sufficient soil percolation for the wastewater loading rate.
Industrial wastewater generated from industrial operations includes process wastewater, wastewater
from utility operations, run-off from process and materials staging areas and miscellaneous activities
including wastewater from laboratories, equipment maintenance shops, etc. The pollutants in
industrial wastewater may include acids or bases (exhibited as low or high pH), soluble organic
chemicals causing depletion of dissolved oxygen, suspended solids, nutrients (phosphorus, nitrogen),
heavy metals (e.g. cadmium, chromium, copper, lead, mercury, nickel, zinc), cyanide, toxic organic
chemicals, oily materials and volatile materials, as well as pollutants from thermal characteristics of
the discharge (e.g. elevated temperature).
Transfer of pollutants off-site should be minimised through process and engineering controls, as
described below.
Process Wastewater
Wastewater treatment system performance very much depends on the adequacy of its design,
equipment selection as well as proper operation and maintenance. Business partners should:
Seek technical and engineering advice in the design and selection of the appropriate
wastewater treatment systems and technologies.
Provide for proper operation and maintenance of the treatment system, through the
employment of qualified, technically competent and well-trained operators.
Avoid uncontrolled air emissions of volatile chemicals from the wastewater treatment
processes.
Ensure waste residue from wastewater treatment operations are disposed of in compliance
with local regulatory requirements and with due consideration for the protection of public
health and safety.
Stormwater includes any surface run-off and flows resulting from precipitation, drainage or other
sources. Typically, stormwater run-off contains suspended sediments, metals, petroleum
hydrocarbons, Polycyclic Aromatic Hydrocarbons (PAHs), coliform, etc. In order to reduce the need for
stormwater treatment, the following should be applied:
Stormwater should be separated from process and sanitary wastewater streams in order to
reduce the volume of wastewater to be treated prior to discharge.
Surface run-off from process areas or potential sources of contamination should be
prevented.
Where this approach is not practical, run-off from process and storage areas should be
segregated from potentially less contaminated run-off.
Run-off from areas without potential sources of contamination should be minimised (e.g. by
minimising the area of impermeable surfaces) and the peak discharge rate should be reduced
(e.g. by using vegetated swales and retention ponds).
Priority should be given to managing and treating the first flush of stormwater run-off where
the majority of potential contaminants tend to be present.
When water quality criteria allow, stormwater should be managed as a resource, either for
groundwater recharge or for meeting water needs at the facility.
Oil-water separators and grease traps should be installed and maintained as appropriate at
refuelling facilities, workshops, parking areas, fuel storage and containment areas.
Sludge from drains or treatment systems may contain elevated levels of pollutants and should
be disposed of in compliance with local regulatory requirements.
Sanitary wastewater from industrial sites may include effluents from domestic sewage, food service,
and laundry facilities serving site employees. Miscellaneous wastewater from laboratories, medical
infirmaries, water softening etc. may also be discharged to the sanitary wastewater treatment system.
In order to properly manage sanitary wastewater, business partners should:
Segregate wastewater streams to ensure compatibility with selected treatment option
(e.g. septic system which can only accept domestic sewage)
Segregate and pre-treat oil and grease containing effluents (e.g. through the use of a grease
trap) prior to discharge into sewer systems.
In any case, if necessary, a specific wastewater discharge permit must be obtained and
complied with and monitored for adherence.
Sludge from sanitary wastewater treatment systems should be disposed of in compliance with
local regulatory requirements, in the absence of which disposal has to be consistent with
protection of public health and safety and conservation and long-term sustainability of water
and land resources.
Air emissions from wastewater treatment operations may include hydrogen sulfide, methane, ozone
(in the case of ozone disinfection), volatile organic compounds (e.g. chloroform generated from
chlorination activities and other volatile organic compounds (VOCs) from industrial wastewater),
gaseous or volatile chemicals used for disinfection processes (e.g. chlorine and ammonia), and
bioaerosols. Odours from treatment facilities can also be a nuisance to workers and the surrounding
community. Recommendations for the management of emissions are given in the Air Emissions
section of these Guidelines (Section 4.3) and in the adidas Groups Environmental Best Practices
Guidelines 2005.
Sludge from a waste treatment plant needs to be evaluated to establish whether it constitutes a
hazardous or a non-hazardous waste and managed accordingly. See also the Waste Management
section of these Guidelines (Section 4.1).
4.2.9 Monitoring
A wastewater and water quality monitoring programme with adequate resources and management
oversight should be developed and implemented to meet the objective/s of the monitoring
programme. The wastewater and water quality monitoring programme should consider the following
elements:
Monitoring Parameters
The parameters selected for monitoring should be indicative of the pollutants of concern from the
process and should include parameters that are regulated under compliance requirements.
Monitoring Locations
The monitoring location should be selected with the objective of providing representative monitoring
data. Effluent sampling stations may be located at the final discharge as well as at strategic upstream
points prior to the merging of different discharges. Process discharges should not be diluted prior to
or after treatment with the objective of meeting the discharge or ambient water quality standards.
Data Quality
Monitoring programmes should apply internationally approved methods for sample collection,
preservation and analysis. Sampling should be conducted by, or under the supervision of, trained
individuals. Analysis should be conducted by entities permitted or certified for this purpose. Sampling
and Analysis Quality Assurance/Quality Control (QA/QC) plans should be prepared and implemented.
QA/QC documentation should be included in monitoring reports.
Wastewater treatment facility operators may be exposed to physical, chemical and biological hazards
depending on the design of the facilities and the types of wastewater effluents managed. Examples of
these hazards include the potential for trips and falls into tanks, confined space entries for
maintenance operations and inhalation of VOCs, bioaerosols and methane, contact with pathogens and
vectors and use of potentially hazardous chemicals, including chlorine, sodium and calcium
hypochlorite and ammonia. Please refer to the guidance on occupational health and safety given in the
adidas Groups Health & Safety Guidelines 2010.
Emissions of air pollutants can occur from a wide variety of industrial activities and can come from a
single source (e.g. a flue or stack from a boiler or furnace) or from multiple sources (e.g. the
application of solvents in a production line). Wherever possible, business partners should avoid,
minimise and control adverse impacts of air emissions on human health, safety, and the environment.
Factories with significant sources of air emissions and potential for significant impacts on air quality
should prevent or minimise impacts by ensuring that emissions do not reach or exceed relevant local
or national air quality standards, or in their absence of such standards, the current World Health
Organizations (WHO) Air Quality Guidelines or other internationally recognised guidance. Reference
should also be made to Table 7.1 of the adidas Groups Health & Safety Guidelines 2010.
To ensure compliance with the applicable local or national standards, air emissions should be
regularly monitored and samples tested in government-approved laboratories.
Point sources are discrete, stationary, identifiable sources of emissions that release pollutants to the
atmosphere. They are typically associated with the combustion of fossil fuels, which may result in the
release of air pollutants such as nitrogen oxides (NOx), sulfur dioxide (SO2), carbon monoxide (CO),
and particulate matter (PM), but may also include other air pollutants depending on the industrial
processes involved.
Emissions from point sources should be avoided and controlled through the combined application of
process modifications and emissions controls, including the proper design of the stack height. The
stack height should be designed to avoid excessive ground level concentrations due to downwash,
wake, and eddy effects, and to ensure reasonable diffusion to minimise impacts. For factories where
there are multiple sources of emissions, stack heights should consider emissions from all other
sources.
Fugitive source air emissions refer to emissions that are distributed spatially over a wide area and are
not confined to a specific discharge point. The two main types of fugitive emissions are VOCs and
particulate matter (PM). Factories with potentially significant fugitive sources of emissions must carry
out regular ambient quality testing as part of their monitoring practices.
Open burning of solid wastes, whether hazardous or non-hazardous, is not a good practice and should
be avoided.
Equipment leaks include valves, fittings and elbows which are subject to leaks under pressure. The
recommended prevention and control techniques for VOC emissions associated with equipment leaks
include equipment modifications and implementing a leak detection and repair (LDAR) programme by
regularly monitoring to detect leaks and implementing repairs within a pre-defined time period.
For VOC emissions associated with handling of chemicals in open vats and mixing processes, the
recommended prevention and control techniques include:
Substitution of less volatile substances, such as water-based solvents
Collection of vapours through air extractors and subsequent treatment of gas stream by
removing VOCs with control devices such as condensers or activated carbon absorption
Collection of vapours through air extractors and subsequent treatment with destructive
control devices, for example, catalytic incinerators which reduce VOCs from process exhaust
gases exiting paint spray booths, ovens and other process operations
Use of floating roofs on storage tanks to reduce the opportunity for volatilisation by
eliminating the headspace present in conventional storage tanks.
Operators responsible for cleaning and disposing of dust and baghouse waste should be provided with
the proper safety training and PPE (Personal Protective Equipment), i.e. apron, head cover and mask.
All residues should be properly and safely disposed of to an authorised waste facility.
HBFCs should only be considered as interim/bridging alternatives as determined by the host country
commitments and regulations.
4.4 Noise
This section of the Guidelines addresses impacts of noise beyond the property boundary of the
facilities. Please also see the adidas Groups Health & Safety Guidelines on noise as an occupational
health concern.
Noise prevention and mitigation measures should be applied where predicted or measured noise
impacts from a facility or operation exceed the applicable noise level guideline at the most sensitive
point of reception. A point of reception or receptor may be defined as any point on the premises
occupied by persons where extraneous noise and/or vibration are received.
The preferred method for controlling noise from stationary sources is to implement noise control
measures at source. However, methods for prevention and control of sources of noise emissions will
depend on the source and proximity of receptors.
To ensure compliance with the applicable local or national standards, noise levels should be regularly
monitored. In the absence of any local guidelines or standards, noise impacts should not exceed the
levels presented in Table 4.2 or result in a maximum increase in background levels of 3dB at the
nearest receptor location off-site.
Industrial; commercial 70 70
4.4.3 Monitoring
Noise monitoring may be carried out for the purposes of establishing the existing ambient noise levels
in the area surrounding the facility or to verify operational noise levels. Noise monitoring programmes
should be designed and conducted by trained personnel. Typical monitoring periods should be
sufficient for statistical analysis and may last 48 hours with the use of noise monitors that should be
capable of logging data continuously over this time period, or hourly, or more frequently, as
appropriate.
Additional information on noise reduction options and good practice on noise minimisation on-site can
be found in Section 11.0 of the adidas Groups Health and Safety Guidelines and in Chapter 5 of the
adidas Groups Guide to Environmental Best Practices. For guidance on the measurement and
management of noise and its impact on communities, please refer to the World Health Organizations
(WHO) Guidelines for Community Noise 1999.
Land is considered contaminated when it contains hazardous materials or oil concentrations above
background or naturally occurring levels. The source of contamination may be due to historic or
current site activities, including accidents and the poor handling, storage and disposal of hazardous
materials or waste. Contaminated lands may involve surface soils or subsurface soils that, through
leaching and transport, may affect groundwater, surface water and adjacent sites. Where subsurface
contaminant sources include volatile substances, soil vapour may also become a transport and
exposure medium and create potential for contaminant infiltration of indoor air spaces of buildings.
Contaminated lands should be managed to avoid the risk to human health and ecological receptors.
The preferred strategy for land decontamination is to reduce the level of contamination at the site
while preventing the human exposure to contamination.
To determine whether risk management actions are warranted, the following simple assessment
approach should be applied to establish whether the three risk factors of Contaminants, Receptors,
and Exposure Pathways co-exist, or are likely to co-exist, at the production site:
1. Contaminant(s): Presence of hazardous materials, waste, or oil in any environmental media in
potentially hazardous concentrations
2. Receptor(s): Actual or likely contact of humans, wildlife, plants and other living organisms
with the contaminants of concern
3. Exposure pathway(s): A combination of the route of migration of the contaminant from its
point of release (e.g. leaching into potable groundwater) and exposure routes (e.g. ingestion,
transdermal absorption), which would allow receptor(s) to come into actual contact with
contaminants.
When the three risk factors are considered to be present (in spite of limited data) under current or
foreseeable future conditions, the following steps should be followed:
1. Risk screening
2. Interim risk management
3. Detailed quantitative risk assessment
4. Permanent risk reduction measures.
Where contaminated soil and/or groundwater is required, the cost of cleaning and the length of time
required to do so escalates dramatically as the level of clean-up required increases. Thus, it is in the
best interest for our business partners to prevent contamination at the outset. If remediation is,
however, necessary, reference should be made to local or national standards on soil and groundwater
clean-up requirements.
On-site treatment for contaminated soils and groundwater can take the form of in-situ and ex-situ
treatments, the choice of which depends on specific site conditions. In-situ treatment does not require
any removal of the contaminated soil or groundwater. Conditions where such a treatment method is
applicable include the treatment of soils beneath or in close proximity to buildings and in soil
conditions that are amenable to these technologies.
In other circumstances, the soils may need to be excavated or the contaminated groundwater pumped
out for treatment which may include the addition of microbial agents or chemical catalysts. This
treatment generally involves mechanical mobile processes which consist of screening and blending.
Off-site treatment of soils can also take the form of standard landfill disposal options or treatment at
licensed facilities (where available).
Business partners should comply fully with local or national standards and laws for the evaluation and
mitigation of soil and groundwater contamination. In the absence of local guidance or regulation, they
should apply the Dutch List which is a widely referenced international standard:
http://www.epd.gov.hk/eia/register/permit/latest/figure/vep159appendixa.pdf
Site operatives should be mindful of the occupational exposures that could arise from working in close
contact with contaminated soil or other environmental media (e.g. groundwater, wastewater,
sediments and soil vapour). Occupational health and safety precautions should be exercised to
minimise exposure, as described in Chapter 6 of the adidas Groups Guide to Environmental Best
Practices 2005 and Section 5 (Chemical Safety Management) and 6 (Use of Hazardous Materials in
Production) in the Health & Safety Guidelines. In addition, personnel carrying out contaminated land
site investigation and remediation activities should receive specific health and safety training and have
the correct PPE.
As a basic principle, the adidas Group expects its business partners to identify and manage the risks
and hazards associated with their operations and activities so as to prevent or minimise any impacts
to their surrounding ecosystems, animals and people.
Risk assessment has become a tool that is widely used in various professions and industries to
examine the risks of very different natures. At its core, risk assessment is a procedure by which risks
associated with inherent hazards of a process or a situation is estimated either qualitatively or
quantitatively, allowing the assessor to decide if enough precautions have been taken or whether
more measures are required to address the identified risk.
An environmental risk assessment (ERA) examines the risks that arise from technology which could
threaten ecosystems, animals and people. While ERAs may be broken down further to occupational
health, ecological and ecotoxicological risk assessments, the main principal is to make sure that the
natural and built environment, animals and people do not get hurt or become ill. Ill health and
accidents can ruin lives and also affect your business if production is lost, or if property or machinery
is damaged because of them.
The following definitions, which can also be found in the adidas Group Health & Safety Guidelines,
apply when conducting a risk assessment:
Hazard
A hazard is anything that has the potential to cause harm (for example chemicals, electricity, working
at height, etc.).
Hazard classes have been defined in Table 18.1 of the adidas Groups Health & Safety Guidelines and
should be referred to in conducting any ERA.
Risk
A risk is the likelihood (great or small) of harm being done.
Damage Indicators
There are six major indicators that are commonly assessed in an ERA and cover both human health
and ecosystems. The indicators can be mapped onto the following table (Table 5.1) for the purpose of
assessing risk:
1 2 3 4 5
0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0
1 10 100 1000
a
0.1 1 10 100
d
Risk Factors
A risk factor reflects the likelihood of harm being caused. Use a scale of 1-5: 1 as the least likely to
happen, through to 5 as very likely to happen. A category 5 risk would be one with a very high (80% or
more) chance of happening, and a category 1 with a very remote (10% or less) chance of happening.
There are three main criteria that must be reviewed in the process of identifying hazards and the
associated risks in any given area. These are:
Pollutant Potential: How dangerous are the pollutants and in what quantities are they present?
Release Potential: How fast, how far and in what quantities will the pollutants be released and
transported?
Exposure and importance of natural resources (water, soil, air): Can the pollutants reach
natural resources at all? And how great is the extent of any potential damage?
The extent of any combination of these three criteria will define the extent of risk on the environment
and thus, at most, risk assessments can only give estimates to the hazards. A residual risk, and with it
a certain degree of uncertainty, will always remain. For example, chemicals can contaminate soil and
groundwater as well as impact people, but the risk of them doing so when they are properly stored
(i.e. in storage containers appropriate for the type of chemical, segregated, etc.) and there is a
chemical management plan in place is low, provided that the workers also undergo regular training
on chemical management and proper PPE is worn.
Business partners are expected to review the detailed discussion on Risk Assessment in the adidas
Groups H&S Guidelines.
More complete guidance on how to conduct an environmental risk assessment can be found at:
http://www.eea.europa.eu/publications/GH-07-97-595-EN-C2
Activity/Process Description:
Acceptable? If not:
Probability X Impact = Rating
Consequence/Hazards Existing Control Identify with number
No. Deviation Cause (see matrix at the end of the
Involved measures and go on to the next
document)
table
1 0
2 0
3 0
4 0
5 0
6 0
7 0
Do any procedures/processes/plans relating to the task need to be amended or updated in light of your risk assessment findings? Yes No
If Yes give details:
,
Action Plan
Management Confirmation
I have noted the above assessment and will take appropriate steps to ensure all the actions raised are completed satisfactorily.
Name (Block Capitals):
(Manager responsible for the activity)
Signed: Date:
NB If the above statement cannot be verified then a re-assessment will be required to confirm that there has been no significant change to the activity/
process.
We expect our business partners to ensure that materials supplied to the adidas Group are in full
compliance with actual local laws and regulations regarding environmental and product safety.
Furthermore, we require our business partners to avoid the intentional use of those substances which
are listed in the adidas Group Policy for the Control and Monitoring of Hazardous Substances (A-01)
and to comply with best practice standards.
We actively encourage our business partners to take a proactive stance in improving the
environmental impact of the materials they supply. Improving the environmental impact means to:
Ensure that materials and components supplied are non-toxic in use and disposal and using
them in manufacturing products does not involve toxic releases or damaging ecosystems.
Strive to make materials which come from renewable and organic resources that are
recyclable or biodegradable.
Manufacture product components and materials under the best possible environmental
conditions and to use the best available technology.
Whilst the A-01 policy addresses the presence of restricted substances in the final product, the adidas
Group has also issued a ban on the use of certain chemicals in order to minimise occupational health
risks to workers. The following chemicals are prohibited due to their recognised high toxicity, their
rapid absorption through skin, and/or the extreme difficulty of exposure control (CAS numbers
indicated in parenthesis).
Note: For information on the associated Material Safety Data Sheet (MSDS) information for each of the
chemicals listed above, please refer to http://msds.chem.ox.ac.uk/newcas.html.
Where banned chemicals are used in the production process due to technical limitations, the supplier
shall develop a comprehensive remediation action plan to address the removal and replacement of
the banned chemical(s) with a safer alternative for SEA approval.
The reporting period is for each full calendar year, e.g. January 1, 2009 to December 31, 2009.
8 Indirect energy electricity. Indicate carbon emission factor specified for the grid CO2 (kg)
used at your local site, e.g. CO2 (kg) per MWh per MWh
9 Indirect energy - district heat. Indicate carbon emission factor specified for the grid CO2 (kg)
used at your local site, e.g. CO2 (kg) per MWh per MWh
Resources / Materials
11 Paper consumption in tonnes per year Tonne
EMISSIONS
12 Emissions from fossil fuel consumption are reported under Resources above.
Emissions/ Wastewater Discharge
13 Wastewater discharge m3/h
PRODUCTION VOLUMES
26 Total units of production made: Number of
- Product category X pieces;
tonne
- Product category Y
- Etc.
IMPROVEMENT PROGRAMMES
27 Please state what improvements you have made in the environmental area over the
past two years (2007 (2008, etc.) and 2008 (2009, etc.)).
Example: Water consumption. Savings of 12% in two years. Actions taken were: XXYY.
Investments were: ZZAA. Payback time was: AABB.
28 Improvement 1:
29 Improvement 2:
30 Improvement 3: