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Document 32017D2285
Commission Decision (EU) 2017/2285 of 6 December 2017 Amending the user's guide setting out the steps needed to participate in EMAS, under Regulation (EC) No 1221/2009 of the European Parliament and of the Council on the voluntary participation by organisations in a Community eco-management and audit scheme (EMAS) (notified under document C(2017) 8072) (Text with EEA relevance. )
Commission Decision (EU) 2017/2285 of 6 December 2017 Amending the user's guide setting out the steps needed to participate in EMAS, under Regulation (EC) No 1221/2009 of the European Parliament and of the Council on the voluntary participation by organisations in a Community eco-management and audit scheme (EMAS) (notified under document C(2017) 8072) (Text with EEA relevance. )
Commission Decision (EU) 2017/2285 of 6 December 2017 Amending the user's guide setting out the steps needed to participate in EMAS, under Regulation (EC) No 1221/2009 of the European Parliament and of the Council on the voluntary participation by organisations in a Community eco-management and audit scheme (EMAS) (notified under document C(2017) 8072) (Text with EEA relevance. )
C/2017/8072
OJ L 328, 12.12.2017, p. 38–86
(BG, ES, CS, DA, DE, ET, EL, EN, FR, HR, IT, LV, LT, HU, MT, NL, PL, PT, RO, SK, SL, FI, SV)
No longer in force, Date of end of validity: 09/11/2023; Implicitly repealed by 32023D2463 The end of validity date is based on the date of publication of the repealing act taking effect on the date of its notification. The repealing act was notified but the date of notification is not available on EUR-Lex – the date of publication is used instead.
12.12.2017 |
EN |
Official Journal of the European Union |
L 328/38 |
COMMISSION DECISION (EU) 2017/2285
of 6 December 2017
Amending the user's guide setting out the steps needed to participate in EMAS, under Regulation (EC) No 1221/2009 of the European Parliament and of the Council on the voluntary participation by organisations in a Community eco-management and audit scheme (EMAS)
(notified under document C(2017) 8072)
(Text with EEA relevance)
THE EUROPEAN COMMISSION,
Having regard to the Treaty on the Functioning of the European Union,
Having regard to Regulation (EC) No 1221/2009 of the European Parliament and of the Council of 25 November 2009 on the voluntary participation by organisations in a Community eco-management and audit scheme (EMAS), repealing Regulation (EC) No 761/2001 and Commission Decisions 2001/681/EC and 2006/193/EC (1), and in particular Articles 46(5) thereof,
Whereas:
(1) |
The objective of EMAS is to promote continuous improvements in the environmental performance of organisations by the establishment and implementation of an environmental management system, the evaluation of the performance of such a system, the provision of information on environmental performance, an open dialogue with the public and other interested parties and the active involvement of employees. |
(2) |
Interested organisations should receive additional information and guidance about the steps needed to participate in EMAS. This information and guidance shall be kept up to date based on the experience gained in the operation of EMAS and in response to additional needs for guidance identified. |
(3) |
The following additional needs for guidance have been identified: definition of a geographic location in the context of the definition of a site, guidance on how the sectoral reference documents should be taken into account and guidance related to the utilisation of a sampling method for verification of multisite organisations. |
HAS ADOPTED THIS DECISION:
Article 1
The Annex to the Commission Decision 2013/131/EU (2) shall be replaced by the text set out in the Annex to this Decision.
Article 2
This Decision is addressed to the Member States.
Done at Brussels, 6 December 2017.
For the Commission
Karmenu VELLA
Member of the Commission
(1) OJ L 342, 22.12.2009, p. 1.
(2) Commission Decision 2013/131/EU of 4 March 2013 establishing the user's guide setting out the steps needed to participate in EMAS, under Regulation (EC) No 1221/2009 of the European Parliament and of the Council on the voluntary participation by organisations in a Community eco-management and audit scheme (EMAS) (OJ L 76, 19.3.2013, p. 1).
ANNEX
‘ANNEX I
I. INTRODUCTION
It is an objective of EU environmental policy to encourage all kinds of organisations to use environmental management systems and reduce their environmental impacts. Environmental management systems are one of the possible tools for companies and other organisations to improve their environmental performance whilst saving energy and other resources. In particular, the EU would like to encourage organisations to participate in the Eco-Management and Audit Scheme (EMAS) which is a management tool for companies and other organisations to evaluate, report and improve their environmental performance.
EMAS was established in 1993 and evolved over time. The EMAS Regulation (1) provides the legal basis for the scheme and the latest revision dates back to 2009.
This EMAS User Guide has been prepared according to the requirements of Article 46.5 of the EMAS Regulation. This document aims to deliver clear, simple advice for organisations interested in EMAS. It is intended to offer step-by-step instructions that are easy to follow. The guide outlines the main elements and steps to be undertaken by an organisation that intends to participate in the scheme. The document aims to increase the overall uptake of the EMAS management system by facilitating the entry of organisations into the scheme. It is also important to keep in mind the general objective of the European Regulation, which is to harmonise implementation across all Member States and create a common legislative framework. For specific EMAS Global related issues the reader is referred to the Commission Decision 2011/832/EU (2), of 7 December 2011 concerning a guide on EU corporate registration, third country and global registration under Regulation (EC) No 1221/2009.
II. WHAT IS THE ECO-MANAGEMENT AND AUDIT SCHEME (EMAS)?
EMAS is a voluntary tool available to any organisation operating in any economic sector within or outside the European Union that wants to:
— |
assume environmental and economic responsibility; |
— |
improve its environmental performance; |
— |
communicate its environmental results to society and stakeholders in general. |
Below is a step-by-step outline on what needs to be done to register for the scheme and implement it.
Organisations that register with EMAS have to:
— |
prove compliance with environmental legislation; |
— |
make a commitment to continually improving their environmental performance; |
— |
show they have an open dialogue with all stakeholders; |
— |
involve employees in improving the organisation's environmental performance; |
— |
publish and update a validated EMAS environmental statement for external communication. |
There are some further requirements. Organisations have to:
— |
conduct an environmental review (including the identification of all direct and indirect environmental aspects); |
— |
register with a competent body after successful verification of their organisation. |
Once registered, organisations are entitled to use the EMAS logo.
III. COSTS AND BENEFITS OF IMPLEMENTING EMAS
In general, environmental management systems such as EMAS help organisations to improve resource efficiency, reduce risks and set an example with their public declaration of good practice. The costs of implementing a scheme are outweighed by the savings.
Benefits
A study (3) has been carried out on the costs and benefits of registering with EMAS. A survey was conducted where those taking part were asked to select the impacts that had been most positive from a given list. ‘Energy & resource savings’ ranked top (21 %), as shown in figure 1. This was followed by ‘reduction in negative incidents’ (18 %) and ‘improved stakeholder relationships’ (17 %).
Figure 1
Benefits of implementing EMAS (% all responses)
Improved stakeholder relationships 17 %
Reduction in negative incidents
18 %
Increased market opportunities
12 %
Productivity improvement 11 %
Financial savings 9 %
Energy & resource savings 21 %
Other 4 %
Improved staff recruitment/ retention 8 %
More efficiency savings
The benefit ‘Energy and resource savings’ ranked top. For organisations of all sizes, there was evidence that energy savings alone exceeded the annual costs of maintaining EMAS. This suggests that larger organisations should easily be able to recover the costs of implementing EMAS.
Fewer negative incidents
This benefit ranked second. Several factors, such as the lower incidence of breaches of environmental law, came into play. This obviously links up with benefits in terms of better relations with regulatory authorities.
Better relations with stakeholders
Organisations rated better relations with stakeholders as a key benefit, particularly in the case of public administration and service companies.
More market opportunities
Registering for EMAS can improve business. It can help retain existing customers and win new business. For public procurement, having an EMAS environmental management system can be an advantage. Though organisations involved in public procurement cannot explicitly require bidders to be EMAS-registered, companies that are registered can use this to show they have the technical means to fulfil contractual environmental management requirements.
Moreover, organisations may encourage their suppliers to have an environmental management system in place as part of their own environmental policy. Being EMAS-registered may make internal business-to-business procedures easier for both parties.
Regulatory relief
EMAS-registered organisations may be entitled to regulatory relief. There may be benefits for companies involved in manufacturing sectors, with advantages under Integrated Pollution Prevention and Control legislation (4).
Several Member States also offer advantages to EMAS-registered organisations regarding state and regional environmental laws and regulations. Such benefits may, for instance, involve simplified reporting obligations; fewer inspections, lower waste fees and longer periods between permit renewals.
Examples include: a 50 % reduction in waste fees; a 20-30 % reduction in fees for licensing procedures; a reduction of up to 100 % in fees for monitoring and enforcement under national law, a 30 % reduction in fees for public services performed by government agencies, a 30 % reduction in fees for surface water licensing procedures, groundwater extraction permits and for landfill licensing procedures. There are also advantages when it comes to administration of monitoring and handling of hazardous chemicals, waste disposal obligations (by not having to demonstrate technical supervision measures) and greenhouse gases monitoring.
Costs and benefits
Businesses should regard registering for EMAS as an investment. Implementing EMAS involves internal and external costs, such as consultancy support, human resources to implement and follow up measures, inspections, registration fees, etc.
Actual costs and benefits vary widely, depending on, for example, the size and activities of the organisation, the current state of play on environmental management practices, the specific country, etc. But in general, EMAS does lead to significant savings. Various studies have shown that organisations recoup implementation costs through increased revenue within a fairly short time, between one and two years in most cases (5) (6) (7) (8) (9).
Table 1
Costs and potential annual efficiency savings in EMAS (10)
(EUR) |
|||
Organisation size (11) |
Potential annual efficiency savings |
First year implementation costs (12) of EMAS |
EMAS Annual costs (13) |
Micro |
3 000 – 10 000 |
22 500 |
10 000 |
Small |
20 000 – 40 000 |
38 000 |
22 000 |
Medium |
Up to 100 000 |
40 000 |
17 000 |
Large |
Up to 400 000 |
67 000 |
39 000 |
Data on ‘Potential annual efficiency savings’ are based on energy savings only. No data are available on resource efficiency savings |
|
|
|
Source:‘Costs and Benefits of EMAS to Registered Organisations’, study for European Commission, 2009. |
The EMAS ‘Toolkit for small organisations’ (14) provides many other examples of cost/benefit savings.
As a whole, micro and small organisations face proportionally higher fixed and external costs than medium or large organisations, since the latter benefit from economies of scale, with a higher proportion of costs borne internally by environment departments, and lower external costs as they have less need for consultants. However, even very large organisations are advised to investigate implementation costs in detail.
EMAS and energy management systems such as EN 16001 and ISO 50001 are quite similar. As management of energy use is part of EMAS, EMAS registered organisations already improve their energy efficiency, consequently they fulfil most EN 16001 and ISO 50001 requirements. Therefore this can also result in cost reductions.
Organisations considering EMAS registration should also take into account the technical and financial support or subsidies that Member States, national, regional or local authorities and EMAS Competent Bodies offer.
IV. EMAS REGULATION
The EMAS scheme was established in Regulation (EC) No 1221/2009 (also known as EMAS III) and is directly applicable in all Member States.
1. GENERAL
1.1. SCOPE
Since 2001, any public or private organisation can implement EMAS. With EMAS III, the scheme is also available to non-European organisations or European companies operating in non-European countries. On the latter issue, there is specific guidance on EU corporate registration, third country and global registration.
‘ “Organisation” means a company, corporation, firm, enterprise, authority or institution, located inside or outside the Community, or part or combination thereof, whether incorporated or not, public or private, which has its own functions and administration.’
EMAS can be implemented in one, several or all sites belonging to private or public organisations in any sector of activity (15). The smallest entity that can be registered is a site.
‘ “Site” means a distinct geographic location under the management control of an organisation covering activities, products and services, including all infrastructure, equipment and materials; a site is the smallest entity to be considered for registration.’
A ‘distinct geographic location’ should be understood as:
‘A physical continuity of land, buildings, equipment or infrastructures, possibly interrupted by external elements provided that functional and organizational continuity of activities is assured.’
1.2. REQUIREMENTS
The general procedure for implementing EMAS can be summarised as follows:
(1) |
The organisation should start with an environmental review, an initial analysis of all activities the organisation carries out, to identify relevant direct and indirect environmental aspects, and the applicable environmental legislation; |
(2) |
Then an environmental management system needs to be implemented, in line with the requirements of EN ISO 14001 (Annex II of EMAS Regulation); |
(3) |
The system needs to be checked by carrying out internal audits and a management review; |
(4) |
The organisation writes an EMAS environmental statement; |
(5) |
The environmental review and the environmental management system are verified and the statement is validated by an accredited or licensed EMAS verifier; |
(6) |
Once the organisation has been verified, it submits an application for registration to the Competent Body. |
In accordance with the Article 46 of the EMAS Regulation the European Commission is developing ‘Sectoral Reference Documents’ (16) (SRDs) for a number of priority sectors in consultation with Member States and other stakeholders.
Each document includes the following elements:
— |
best environmental management practice; |
— |
environmental performance indicators for the specific sectors concerned; |
— |
where appropriate, benchmarks of excellence and rating systems identifying environmental performance levels. |
When available for their specific sector, EMAS registered organisations are to take SRDs into account at two different levels:
1. |
When developing and implementing their environmental management system in light of the environmental reviews (Article 4(1)(b)); |
2. |
When preparing the environmental statement (Article 4(1)(d) and Article 4(4)). |
EMAS participation is an ongoing process. Every time an organisation reviews its environmental performance and plans improvements it shall consult the SRD (when available) on specific topics to find inspiration about which issues to tackle next in a step-wise approach.
Figure 2
General schedule for EMAS implementation
EMAS environmental statement
Registration: Competent Body
Verification and Validation
Internal audit/ Management Review
* General requirements
* Environmental policy
* Planning
* Implementation and operation
* Checking requirements in place
Environmental management system
Environmental review
Table 2
Indicative time schedule for the implementation of EMAS. The time involved in each activity is an average, which can be shorter or longer depending on the Member State, the organisation size, etc.
EMAS |
Month 1 |
Month 2 |
Month 3 |
Month 4 |
Month 5 |
Month 6 |
Month 7 |
Month 8 |
Month 9 |
Month 10 |
Environmental review |
X |
X |
|
|
|
|
|
|
|
|
Environmental management system |
|
X |
X |
X |
X |
X |
X |
|
|
|
General requirements |
|
X |
|
|
|
|
|
|
|
|
Environmental policy |
|
X |
|
|
|
|
|
|
|
|
Planning: Environmental Objectives and targets |
|
X |
|
|
|
|
|
|
|
|
Planning: Environmental programme |
|
|
X |
X |
X |
|
|
|
|
|
Implementation and operation: Resources, roles, responsibility and authority |
|
|
|
|
X |
|
|
|
|
|
Implementation and operation: Staff competence, training and awareness, including employee involvement |
|
|
|
|
X |
|
|
|
|
|
Implementation and operation: Communication (internal and external) |
|
|
|
|
|
X |
|
|
|
|
Implementation and operation: Documentation and control of documents |
|
X |
X |
X |
X |
X |
|
|
|
|
Implementation and operation: Operational control |
|
|
|
|
|
X |
X |
|
|
|
Implementation and operation: Emergency plans |
|
|
|
|
|
|
X |
|
|
|
Checking: Monitoring and measuring, evaluation of compliance, non-conformity, corrective and preventive action, control of records |
|
|
|
|
X |
X |
X |
|
|
|
Checking: Internal Audit |
|
|
|
|
|
|
X |
X |
|
|
Management review |
|
|
|
|
|
|
|
X |
|
|
EMAS environmental statement |
|
|
|
|
|
|
|
|
X |
|
Verification and Validation |
|
|
|
|
|
|
|
|
X |
|
Registration |
|
|
|
|
|
|
|
|
|
X |
2. HOW TO IMPLEMENT EMAS
2.1. ENVIRONMENTAL REVIEW
The first step in implementing EMAS properly is to conduct a thorough analysis of an organisation's internal structure and activities. The aim is to identify environmental aspects (as defined below) associated with environmental impacts. That is the basis for setting up a formal environmental management system.
‘ “Environmental Review” means an initial comprehensive analysis of environmental aspects, environmental impacts and environmental performance related to an organisation's activities, products and services.’
The analysis must include:
— |
Legal requirements that apply to the organisation; |
— |
Identification of direct and indirect environmental aspects; |
— |
Criteria for assessing the significance of the environmental aspects; |
— |
Examination of all existing environmental management practices and procedures; |
— |
Evaluation of feedback after investigation of incidents in the past. |
‘Environmental aspect’ means an element of an organisation's activities, products or services that has or can have an impact on the environment. Environmental aspects may be input related (consumption of raw materials and energy, for instance) or output related (air emissions, waste generation, etc.).
Figure 3
Relation between activities, environmental aspects and environmental impacts
Environmental impacts
Environmental aspects
Activities/ Products/ Services
The organisation needs procedures to ensure that activities identified as significant during the first environmental review are properly followed up later. Environmental aspects and related impacts may change, as may the organisation's activities. If the changes are substantial, the environmental review may have to be updated. An organisation should also be aware of new developments, techniques, research results, etc. to help it reassess the significance of its environmental aspects and the possible need to carry out a new environmental review if its activities change significantly.
What is the procedure for carrying out an environmental review?
Organisations must:
— |
identify environmental aspects stemming from their manufacturing processes, activities or services; and |
— |
establish criteria to assess the significance of these aspects. The criteria need to be comprehensive and it must be possible to verify them independently. |
The organisation should remember that it will have to disclose the environmental aspects it identifies and the results of the evaluation to external stakeholders.
How should environmental aspects be identified?
All relevant information needs to be gathered.
This can mean:
— |
Visiting sites to check process inputs and outputs (taking notes, making drawings as required); |
— |
Collecting location maps and pictures; |
— |
Identifying applicable environmental legislation; |
— |
Collecting all environmental permits, licences and similar documents; |
— |
Checking all sources of information (incoming invoices, counters, data concerning equipment, etc.); |
— |
Checking the use of products (often the purchasing and sales departments are useful starting points); |
— |
Identifying key persons (management and workers). Workers involved in all internal systems should be asked for input; |
— |
Requesting information from subcontractors, who may have a significant influence on an organisation's environmental performance; |
— |
Taking into account past accidents, the results of monitoring and inspections; and |
— |
Identifying start-up and shut down situations and identified risks. |
Both direct and indirect environmental aspects must be taken into account, and the definitions below should be helpful in identifying these:
‘ “direct environmental aspect” means an environmental aspect associated with activities, products and services of the organisation itself over which it has direct management control.’ |
‘ “indirect environmental aspect” means an environmental aspect which can result from the interaction of an organisation with third parties and which can to a reasonable degree be influenced by an organisation.’ |
It is essential to consider indirect aspects. This applies both to the private and public sectors, so local authorities, service companies or financial institutions, for instance, need to extend their review beyond site aspects.
Organisations must be able to show they have identified significant environmental aspects associated with their procurement procedures, and that they have addressed significant environmental impacts associated with these in their management system.
Table 3
Examples of direct and indirect aspects
Environmental aspects |
|||||||||||||||||||||||||||||
Direct aspects |
Indirect aspects |
||||||||||||||||||||||||||||
|
|
Direct environmental aspects have to include the related legal requirements and permit limits, e.g. if specific pollutants are bound to emission limit values or other requirements, those emissions should be considered as direct environmental aspects.
Assessment of environmental aspects
The next step is to associate aspects with their effects or impacts on the environment. Table 4 provides an example of such links.
Table 4
Examples of environmental aspects and impacts
Activity |
Environmental aspect |
Environmental impact |
||||||||||||
Transport |
|
|
||||||||||||
Construction |
|
|
||||||||||||
Office services |
|
|
||||||||||||
Chemical industry |
|
|
Once the aspects and their impacts have been identified, the next step is to conduct a detailed assessment of each to determine significant environmental aspects.
‘ “Significant environmental aspect” means an environmental aspect that has or can have a significant environmental impact.’
The issues to consider when assessing significance are:
(i) |
potential to cause environmental harm; |
(ii) |
fragility of the local, regional or global environment; |
(iii) |
size, number, frequency and reversibility of the aspect or impact; |
(iv) |
existence and requirements of relevant environmental legislation; |
(v) |
importance to stakeholders and employees of the organisation. |
Based on these criteria, the organisation can draw up an internal procedure or use other tools to assess the significance of environmental aspects. Small and medium-sized Enterprises (SMEs) will find that the EMAS SME toolkit (17) provides very useful information.
In assessing the significance of environmental aspects, it is important to take into account not just normal operating conditions, but also start-up, shutdown and emergency conditions. Past, present and planned activities should all be considered.
For each environmental aspect, the corresponding impact should be rated according to:
— |
Magnitude — level of emissions, energy and water consumption, etc.; |
— |
Severity — hazards, toxicity, etc.; |
— |
Frequency/probability; |
— |
Concerns of interested parties; |
— |
Legal requirements. |
Table 5
Assessing environmental aspects
Assessing criteria |
Example |
Which outputs or activities of the organisation may negatively affect the environment? |
Waste: mixed municipal waste, waste packaging, hazardous waste |
Magnitude of aspects which may impact the environment |
Quantity of waste: High, medium, low |
Severity of aspects which may impact on the environment |
Hazardousness of waste, toxicity of materials: High, medium, low |
Frequency of aspects which may impact the environment |
High, medium, low |
Public and employee awareness for the aspects associated to the organisation |
Severe, some, no complaints |
Organisation activities regulated by environmental legislation |
Waste law permit, monitoring obligations |
Note: It is useful to quantify criteria and the overall significance of particular aspects. |
How to check legal compliance
‘ “Legal compliance” means full implementation of applicable legal requirements, including permit conditions, relating to the environment.’
Member States have to ensure that organisations have access to information and assistance on the following issues, at a minimum:
— |
Information on the applicable legal requirements relating to the environment; and |
— |
Identification of the competent enforcement authorities for specific legal requirements relating to the environment. |
The enforcement authorities are required to reply to requests for information, at least from small organisations, on the applicable legal requirements relating to the environment, as well as information on how organisations can meet those legal requirements.
Identifying all applicable legal requirements means taking into account different levels of environmental legislation, if appropriate, such as national, regional or local requirements, including permits and licences.
The organisation must also take into account other relevant requirements, for instance, in procurement conditions, business contracts, voluntary agreements that the organisation has signed or subscribed to, etc.
It is essential to identify legal requirements at this point, so that an organisation can pinpoint any that may not be fulfilled. If necessary, an organisation must then take measures to comply with all relevant environmental legislation (see 2.2.5.2 for evaluation of legal compliance).
2.2. ENVIRONMENTAL MANAGEMENT SYSTEM
‘ “Environmental management system” means the part of the overall management system that includes the organisational structure, planning activities, responsibilities, practices, procedures, processes and resources for developing, implementing, achieving, reviewing and maintaining the environmental policy and managing the environmental aspects.’
2.2.1. General requirements
To start with, the organisation must define and document the scope of its environmental management system.
Each site to be involved in an EMAS registration must comply with all the requirements of EMAS.
The organisation has to set up, document, implement and maintain an environmental management system in accordance with section 4 of EN ISO 14001. If the organisation has implemented an environmental management system (other than ISO 14001) that the Commission has recognised (18), it does not have to repeat items that have already been officially recognised when it seeks to fulfil EMAS requirements.
2.2.2. Environmental policy
‘ “Environmental policy” means the overall intentions and direction of an organisation relating to its environmental performance as formally expressed by top management (…). It provides a framework for action and for the setting of environmental objectives and targets’.
Environmental policy must include the following points:
— |
Commitment to complying with legal and other requirements related to its environmental aspects; |
— |
Commitment to preventing pollution; |
— |
Commitment to continually improving environmental performance. |
The environmental policy is a framework for action and for setting strategic environmental objectives and targets (see below). It needs to be clear and must address the top priorities on which specific objectives and targets can be further defined.
2.2.3. Planning
Once basic underlying issues as described above have been covered, the process moves on to planning.
2.2.3.1. Environmental objectives and targets
‘ “Environmental objective” means an overall environmental goal, arising from the environmental policy, that an organisation sets itself to achieve, and which is quantified where practicable.’
‘ “Environmental target” means a detailed performance requirement, arising from the environmental objectives, applicable to an organisation or parts thereof, and that needs to be set and met in order to achieve those objectives.’
An organisation must draw up and document the objectives and detailed targets for each of the aspects relevant in the organisation, in line with its environmental policy.
Once objectives have been defined, the next step is to set proper targets for them. With targets, it is possible to plan specific actions to be carried out to achieve good environmental management.
Figure 4
Relation between objectives, targets and actions
Action
Target
Objective
An example:
Environmental objective |
Minimise hazardous waste generation |
Target |
Reduce the use of organic solvents in the process by 20 % within 3 years |
Action |
Reusing solvents whenever possible Recycling organic solvents |
Objectives and targets should be measurable where possible, and consistent with an organisation's environmental policy. The `SMART` criteria are useful:
— |
Specific — each target should address a single issue; |
— |
Measurable — each target should be expressed quantitatively; |
— |
Achievable — it should be possible to meet the targets; |
— |
Realistic — targets should be demanding and drive continuous improvement, but not overly ambitious. They can always be revised once they have been met; |
— |
Time-bound — there should be a deadline for achieving each target. |
When available for their specific sector, organisations should use relevant elements of the Sectoral Reference Documents as referred to in Article 46 of the EMAS Regulation. These should be used when defining and reviewing the environmental targets and objectives of the organisation in accordance with the relevant environmental aspects identified in the environmental review. However meeting the identified benchmarks of excellence is not mandatory because EMAS leaves the assessment of the feasibility of the benchmarks and of the implementation of the best practices, in terms of costs and benefits, to the organisations themselves.
2.2.3.2. Environmental programme
‘ “Environmental Programme” means a description of the measures, responsibilities and means taken or envisaged to achieve environmental objectives and targets and the deadlines for achieving the environmental objectives and targets.’
The environmental programme is a tool to help the organisation plan and implement improvements from day to day. It should be kept up to date, and detailed enough to give an overview of progress towards meeting targets. The programme should specify who is responsible for achieving objectives and targets, as well as details of the resources and timeframes involved. Resources themselves (e.g. financial, technical or personnel means) cannot be environmental objectives.
In practice, the programme is often drawn up in tabular form, covering the following:
— |
environmental objectives, linked to direct and indirect aspects; |
— |
specific targets to achieve objectives; and |
— |
actions, responsibilities, means and timeframe for each target:
|
Both direct and indirect aspects should be taken into account in drawing up the programme. The organisation should commit itself to improving its environmental performance continuously.
When deciding on which actions to implement to improve their environmental performance, the organisations should take into account the relevant elements of the Sectoral Reference Documents as referred to in Article 46 of the EMAS Regulation, when available for their sector.
In particular they should consider the relevant best environmental management practices and benchmarks of excellence (which provide an indication of the environmental performance level that is achieved by best performers) to identify measures and actions, and possibly to set priorities, to (further) improve their environmental performance.
However, implementing best environmental management practices or meeting the identified benchmarks of excellence is not mandatory, because EMAS leaves the assessment of the feasibility of the benchmarks and of the implementation of the best practices, in terms of costs and benefits, to the organisations themselves.
2.2.4. Implementation and operation
2.2.4.1. Resources, roles, responsibility and authority
If EMAS is to succeed, then top management must be willing to provide the resources and organisational structures needed to support the system. These include human resources and specialised skills in personnel, organisational infrastructure, technology, as well as financial resources.
The environmental review will have examined existing organisational infrastructure, management practices and procedures. At this point, it is time to adapt internal structures and procedures if necessary.
The organisation's top management must appoint a management representative, i.e., a person ultimately responsible for the environmental management system. Their role is to make sure that all the environmental management system requirements are in place, working and up-to-date, as well as to keep the general management team informed about how the system is working. They should report on its strengths and weaknesses, and on improvements needed.
The representative should be qualified and experienced in environmental issues, environment-related legal requirements, management aspects, working group skills, with leadership and coordination skills. The organisation must ensure these competences are all available within the organisation.
Competence, training and awareness
The organisation has to define the experience and knowledge required among staff for good environmental management performance.
It must draw up, implement and maintain a procedure to identify training needs and do whatever is necessary to ensure that staff involved in the environmental management system has appropriate knowledge of:
— |
The organisation's environment policy; |
— |
Legal requirements and other environmental requirements applicable to the organisation; |
— |
The objectives and targets set up for the organisation as a whole and for their specific work areas; |
— |
Environmental aspects and impacts and the methodology for monitoring them; |
— |
Their roles and responsibilities within the environmental management system. |
Everyone working for the organisation or on its behalf should be aware of their roles within EMAS and the environmental benefits of the system. They should receive, or at least have access to, training on environmental awareness and on the organisation's environmental management system.
Figure 5
Flow chart diagram on training within the environmental management system
Planning of training and awareness activities
Training and awareness activities
Assessment of training and awareness activities
Identification of training and awareness needs
Environmental awareness can be achieved through training or other activities, such as communication campaigns, surveys, etc.
Actively involved employees are a driving force for continuous, successful improvement, and they help to anchor EMAS in the organisation. They can become involved through, for instance, an environmental committee, working groups, by suggestion systems, incentive programmes or other activities.
There should be roles for employees at different levels within the development and implementation of the system. They could, for instance, be involved in:
— |
Identifying environmental aspects; |
— |
Drawing up and revising procedures and/or instructions; |
— |
Proposing environmental objectives and targets; |
— |
Taking part in an internal audit process; |
— |
Drafting the EMAS environmental statement. |
Management must offer on-going feedback to employees, and seek feedback from them.
2.2.4.2. Communication
Good internal and external two-way communication is essential to implement an EMAS-registered environmental management system successfully. The organisation needs to recognise the need to communicate with stakeholders on environmental issues and the value of doing so. It is obliged to make the environmental statement public, and it will need to identify what will be communicated and to whom. It will need to monitor the results of its communication and to determine whether it has been effective.
Internal communication should flow in both directions (top down and bottom up). This can be done by using intranet, brochures, internal publications, newsletters, suggestion boxes, meetings, bulletin boards, etc.
Examples of external communication are the EMAS environmental statement, internet, action days, press releases, brochures and use of the EMAS logo if possible and allowed (19).
2.2.4.3. Documentation and control of documents
There should be documentation on the environmental management system, covering the following:
— |
Environmental policy; |
— |
Environmental objectives and targets; |
— |
Description of the scope of the environmental management system; |
— |
Description of the main elements of the environmental management system; |
— |
Roles, responsibilities and authorities; |
— |
Procedure for managing operational control; |
— |
Operational procedures; |
— |
Work instructions. |
Documentation should be clear and concise to avoid confusion or misunderstanding.
EMAS documents can be integrated into other management systems (quality, energy, health and safety, etc.) or vice versa to optimise them, to avoid duplication and to reduce bureaucracy.
SMEs should aim to offer their staff clear, simple, easy-to-use documentation.
Environmental management manual
This covers the environmental policy, environmental protocols and activities. It should be integrated into the organisation's annual management plan. The manual does not need to be long and complex. It should help staff to understand how the organisation has set up and structured its environmental management system, how the different parts of the environmental management system are interrelated and what the roles of particular individuals are within the scheme. This manual is not obligatory, though most organisations opt to have one.
Procedures
Documents on procedures describe HOW, WHEN and by WHOM, specific actions have to be carried out.
Examples are procedures for:
— |
identifying and evaluating significant aspects; |
— |
managing legal compliance; |
— |
managing the identified significant environmental aspects; |
— |
managing monitoring and measurements; |
— |
managing emergency preparedness; |
— |
managing non-conformities, preventive and corrective actions; |
— |
identifying and managing competence, training and awareness; |
— |
managing communication; |
— |
managing documents; |
— |
managing records; |
— |
managing internal audits. |
Work instructions
Work instructions must be clear and easy to understand. They should explain the relevance of an activity, the environmental risk associated with it, specific training for staff responsible for carrying it out, and how it is to be supervised. It may be useful to illustrate it with pictures, pictograms or other ways of ensuring all employees can readily understand the instructions.
Managing documents
The organisation has to set up, implement and maintain a procedure to manage documents drafted for the environmental management system. Specific attention should be paid to records (see 2.2.5.4).
This will require a procedure to:
Figure 6
Process to manage documents within an environmental management system
Control it
Eliminate the old version
Distribute it among the staff
Approve it
Create an EMS document
Review it and modify it if necessary
The system should ensure that different versions of documents remain available, and that documents remain legible and readily identifiable.
Documents from external sources can be included, as they are often essential to ensuring the environmental management system works correctly. Such documents could include information from local authorities and public administrations, equipment user manuals, health and safety sheets, etc.
2.2.4.4. Operational control
Operational control involves identifying and planning operations that are associated with the significant environmental aspects consistent with the policy, objectives and targets (see figure 7). It might also cover activities such as equipment maintenance, start-up and shutdown, management of onsite contractors, and services provided by suppliers or vendors. There need to be procedures to address identified risks, to set targets and to measure environmental performance (preferably through clear environmental indicators). The procedures must define normal conditions. Abnormal conditions and emergencies must be defined and described. Operational control procedures should be well documented and submitted to internal audits.
Figure 7
Operational control
Set up operating criteria
Control objectives and targets
Environmental aspects
Operational control
2.2.4.5. Emergency preparedness and response
The organisation has to draw up, implement and maintain procedures to identify potential emergencies and potential accidents to:
— |
Avoid the risk of an accident; |
— |
Describe how the organisation responds to accidents; |
— |
Prevent or mitigate associated adverse environmental impacts. |
The emergency plan is essential in industry and in organisations involved in potentially risky activities.
The organisation must periodically review its emergency preparedness (including appropriate training) and its response procedures. It should revise them if necessary, particularly after emergencies or accidents. Procedures should also be tested periodically.
Figure 8
Emergency plans
Periodic revision
Environmental impact evaluation
Identification of potential accidents and emergencies
Emergency plans
Preventive measures
Testing, training and reviewing
2.2.5. Checking
2.2.5.1. Monitoring and measurement
The organisation needs to draw up, implement and maintain a procedure to monitor and measure significant parameters such as air emissions, waste, water and noise regularly to gain added value from the findings. Reporting on core performance indicators is an obligation (see 2.3.2).
Legal requirements on monitoring have to be taken into account, and monitoring criteria such as the frequency of inspections and the methodology must comply with them. Information on these is useful to ensure:
— |
Compliance with legal requirements and regulations; |
— |
Accurate evaluation of environmental performance; |
— |
A complete and transparent EMAS statement. |
Depending on the organisation's needs, other factors can also be measured and monitored:
— |
Significant environmental aspects; |
— |
Environmental policy and objectives; |
— |
Level of awareness among employees, etc. |
Measuring equipment must be calibrated on a regular basis to comply with legislation and to obtain accurate results.
2.2.5.2. Evaluation of legal compliance
Legal compliance is a key requirement of the EMAS regulation and an organisation cannot register without it, so it has to have a procedure to review and evaluate this regularly.
This is best done by making a list of all relevant legislation and specific requirements, then comparing this to the organisation's specific circumstances (see table 6). Larger, more complex organisations may need to use databases or seek external assistance.
If the verifier finds instances of non-compliance that have not been corrected, they are not allowed to validate an environmental statement or to sign the final declaration (Annex VII).
Table 6
Example of simple legal compliance evaluation
Applicable environmental legislation |
Specific requirement |
Status of the organisation |
Result |
||||||||||||
Waste law |
|
|
Get an updated permit |
||||||||||||
Air emissions law |
|
|
OK |
||||||||||||
Noise law |
|
|
OK |
||||||||||||
Water treatment law |
|
|
Correct the situation |
||||||||||||
GHG laws |
|
|
OK. It's possible to sell some emission allowances |
2.2.5.3. Non-conformity, corrective and preventive actions
The organisation has to set up, implement and maintain a procedure for dealing with cases and potential cases of non-conformity, with EMAS requirements.
The procedure must include ways of:
— |
Identifying and correcting the case; |
— |
Investigating the cause and effects of the case; |
— |
Evaluating the need for action to avoid recurrence; |
— |
Recording the results of corrective action taken; |
— |
Evaluating the need for measures to prevent cases of non-conformity; |
— |
Implementing appropriate preventive action to avoid such cases; and |
— |
Reviewing the effectiveness of corrective and preventive action. |
Non-conformity means any kind of non-fulfilment with the basic requirements specified in procedures and technical instructions.
Non-conformities may be the result of human or implementation error. Changes to correct and avoid recurrence must be made as soon as possible.
Non-conformities may be detected through:
— |
Operational control; |
— |
Internal/external audit; |
— |
Management review; or |
— |
As part of daily activity. |
Corrective and preventive actions
The EMAS management representative has to be informed about non-conformities so they can make decisions about taking corrective action, if appropriate.
Where potential non-conformities have been identified, the EMAS management representative has to be informed, so they can make decisions about taking preventive action, if appropriate.
Both corrective and preventive action should be recorded. It may be necessary to change the environmental management system documentation as a result.
2.2.5.4. Control of records
The organisation must set up a system to maintain records to show that it complies with the requirements of its environmental management system.
The organisation must set up, implement and maintain a procedure for managing its records. This should cover issues such as identification, storage, protection, retrieval, retention and disposal of records.
Records have to be and remain identifiable, legible, updated and traceable.
Examples of records:
— |
electricity, water and raw materials consumption; |
— |
waste generated (hazardous and non-hazardous waste); |
— |
greenhouse gases (GHG) emissions; |
— |
incidents, accidents and complaints; |
— |
legal requirements; |
— |
audit reports and management reviews; |
— |
inspection reports; |
— |
significant environmental aspects; |
— |
non-conformities, corrective and preventive actions; |
— |
communication and training; |
— |
suggestions from staff; and |
— |
training and seminars. |
2.2.6. Internal audit
EMAS pays particular attention to the internal audit in Annex III.
‘ “Internal environmental audit” means a systematic, documented, periodic and objective evaluation of the environmental performance of an organisation, management system and processes designed to protect the environment.’
The organisation has to set up an internal audit procedure as part of the management system. This must cover responsibilities and requirements for planning and conducting audits, reporting results and keeping records, the determination of audit criteria, scope, frequency and methods.
The goal of the internal audit is to determine:
— |
if the environmental management system meets the requirements of the EMAS Regulation; |
— |
if it has been properly implemented and maintained; |
— |
to guarantee that the organisation's management gets the information it needs to review the organisation's environmental performance; |
— |
the effectiveness of the environmental management system. |
The audit must be carried out objectively by independent personnel. The internal auditor can be a trained member of the staff or an external person or team.
General rules
— |
Establish an audit programme; |
— |
Define the scope of the audit. This will depend on the size and type of organisation. The scope must specify the subject areas covered, the activities to be audited, the environmental criteria to be considered and the period to be covered in the audit; |
— |
Specify the resources needed to carry out the audit, for example, well-trained personnel with a good knowledge of the activity, technical aspects, environmental aspects, legal requirements; |
— |
Make sure that all the activities in the organisation are carried out in conformity with previously defined procedures; and |
— |
Identify potential new problems and put measures in place to prevent occurrence. |
Internal audit steps
Figure 9
Internal audit steps
3. Reporting findings and conclusions
2. Audit activities
1. Programme and frecquency
AUDIT STEPS
2.2.6.1. Audit programme and audit frequency
The programme must include:
— |
specific goals of the internal audit; |
— |
how to check whether the environmental management system is coherent and conforms with the organisation's policy and programme and fulfils the EMAS requirements; |
— |
compliance with applicable environmental regulatory requirements. |
The organisation must carry out internal audits on a yearly basis to have a proper overview of its significant environmental aspects. The audit cycle, which covers all the organisation's activities, must be completed within three years. Small organisations may extend this period to four years.
The frequency with which any specific activity is audited will vary, depending on:
— |
Nature, scale and complexity of the activities concerned; |
— |
Significance of associated environmental impacts; |
— |
Importance and urgency of the problems detected by previous audits; and |
— |
History of environmental problems. |
As a rule, complex activities with a more significant environmental impact need to be audited more frequently.
For satisfactory results, all staff involved in an internal audit must have a clear idea of the environmental objectives of the exercise and the specific roles of everyone taking part (directors, managers, employees, auditors, etc.).
2.2.6.2. Internal audit activities
It is important to prepare for the internal audit beforehand. First, identify the auditor/audit team. The organisation may use its own staff as auditors, or engage outside auditors. They must be objective and impartial and be properly skilled and trained. The auditor/audit team should:
— |
Prepare a good audit plan, by collecting information on the objective, scope, place and date arranged with the organisation; |
— |
Deliver the audit plan to the organisation sufficiently in advance; |
— |
Draw up checklists; |
— |
Distribute tasks within the audit team. |
For an audit to be meaningful, the audit team must check compliance with environmental legislation, whether objectives and targets have been met, and whether the management system is effective and adequate.
The audit process must include the following steps:
— |
Understanding of the management system; |
— |
Evaluation of the system's strengths and weaknesses; |
— |
Gathering relevant evidence (e.g. data, records, documents); |
— |
Evaluating audit findings; |
— |
Preparing audit conclusions; and |
— |
Reporting audit findings and conclusions. |
2.2.6.3. Reporting audit findings and conclusions
The aim of the audit report is to provide management with:
— |
written evidence concerning the scope of the audit; |
— |
information on the extent to which objectives have been met; |
— |
information on whether objectives are in line with the organisation's environmental policy; |
— |
information on the reliability and effectiveness of the monitoring system; |
— |
proposed corrective actions if required. |
The report must be submitted to the EMAS management representative who finalises corrective actions if non-conformities (including cases of non-compliance, if any) have been identified.
2.2.7. Management review
Top management has to review the management system on a regular basis (at least annually) to ensure it is fit for purpose and effectiveness. The management review needs to be recorded, and records kept.
Content of management review
Inputs:
— |
Results of internal audits including evaluation of legal compliance; |
— |
External communication; |
— |
Complaints; |
— |
Extent to which objectives and targets have been met; |
— |
Status of corrective and preventive actions; |
— |
Follow-up to previous management reviews; |
— |
Changing circumstances, e.g. legal developments, environmental changes; |
— |
Recommendations for improvement. |
Outputs include all decisions and activities, changes to environmental policy, objectives, targets and other aspects of the environmental management system.
2.3. EMAS ENVIRONMENTAL STATEMENT
‘ “Environmental statement” means the comprehensive information to the public and other interested parties regarding an organisation's: structure and activities; environmental policy and environmental management system, environmental aspects and impacts; environmental programme, objectives and targets; environmental performance and compliance with applicable legal obligations relating to the environment.’
The statement is one of the unique characteristics of EMAS compared with other environmental management systems.
For the public, it affirms the organisation's commitment to taking action on the environment.
For the organisation, it is a good opportunity to state what it is doing to improve the environment.
EMAS does set out some minimum requirements for the statement, but the organisation can decide how much detail it wishes to go into, as well as the structure and layout, as long as the content is clear, reliable, credible and correct. It is up to the organisation to decide if it wants to include its environmental statement in its annual report, or other reports, for instance, on corporate social responsibility.
2.3.1. Minimum content for EMAS environmental statement
(1) A clear and unambiguous description of the organisation registering under EMAS and a summary of its activities, products and services and its relationship to any parent organisations as appropriate
Include diagrams, maps, flow charts, aerial photographs, etc. to illustrate the content. NACE codes to describe activities should also be included.
(2) The environmental policy and a brief description of the organisation's environmental management system
A proper description of the system is important to provide clear information about the working structure. The environmental policy has to be included.
(3) A description of all the significant direct and indirect environmental aspects which result in significant environmental impacts of the organisation and an explanation of the nature of the impacts as related to these aspects (Annex I.2 of the EMAS Regulation)
Direct and indirect environmental aspects should be given separately. The impacts of both should be given, using tables or flowcharts.
(4) A description of the environmental objectives and targets in relation to the significant environmental aspects and impacts
Use lists of targets and objectives, as well as indicators to assess progress on improving performance. Include the environmental programme and refer to specific measures taken or planned to improve performance.
(5) A summary of the data available on the performance of the organisation against its environmental objectives and targets with respect to its significant environmental impacts. Reporting shall be on the core indicators and on other relevant existing environmental performance indicators as set out in Section C of Annex IV of the EMAS Regulation
Core indicators focus on six key areas: energy, materials, water, waste, biodiversity (through land use) and emissions (see 2.3.2.2).
The organisation shall also report on its performance according to other more specific indicators related to significant environmental aspects mentioned in the environmental review. (see 2.3.2.3). In case no quantitative data is available to report on significant direct or indirect environmental aspects, organisations shall report their performance on the basis of qualitative indicators.
Where sectoral reference documents (SRDs) as referred to in Article 46 of the EMAS Regulation are available for the specific sector, the organisations should consider the relevant sector-specific environmental performance indicators in the SRD when choosing the indicators (20) to use for their reporting of environmental performance.
(6) Other factors regarding environmental performance including performance against legal provisions with respect to their significant environmental impacts
Use tables and/or graphs comparing legal reference limits to limits measured and/or calculated by the organisation.
It is not always possible to measure environmental performance with data. Soft factors are also relevant, and may include changes in behaviour, improvements in processes and other measures taken to improve environmental performance.
When reporting on these other factors, the organisations should take into account the relevant sectoral reference documents (SRDs) as referred to in Article 46 of the EMAS Regulation. They should therefore mention in their environmental statement how the relevant best environmental management practices and, if available, benchmarks of excellence were used to identify measures and actions, and possibly to set priorities, to (further) improve their environmental performance.
The relevance and applicability of the best environmental management practices and benchmarks of excellence should be assessed by the organisation according to the significant environmental aspects identified by the organisation in its environmental review, as well as technical and financial aspects.
Elements of SRDs (indicators, BEMPs or benchmarks of excellence) not considered relevant to the significant environmental aspects identified by the organisation in its environmental review should not be reported or described in the environmental statement.
(7) A reference to the applicable legal requirements relating to the environment
EMAS requires legal compliance. The environmental statement is an opportunity to state how the organisation achieves this.
Though EMAS-registered organisations should have available an internal list of all relevant legal requirements, it is not necessary to include them all in the environmental statement. An outline is enough in this context.
(8) The name and accreditation or licence number of the environmental verifier and the date of validation
If the organisation publishes its environmental statement as part of another report, it should identify the statement as such and indicate that it has been validated by the environmental verifier. Although it is not mandatory to annex the declaration referred to in Article 25(9) to the EMAS environmental statement is it considered best practise to do so.
2.3.2. Core indicators and other relevant existing environmental performance indicators
2.3.2.1. Core indicators
Organisations have to report on the core environmental performance indicators (also known as key performance indicators) relevant to direct environmental aspects of the organisation. They should also report on other performance indicators relevant to more specific environmental aspects. They should take into account sectoral reference documents (SRDs) where these are available.
Core indicators apply to all types of organisations. They measure performance in the following key areas:
— |
Energy; |
— |
Materials; |
— |
Water; |
— |
Waste; |
— |
Land use with regard to biodiversity; |
— |
Emissions. |
Each core indicator is composed of a figure A (input), a figure B (output) and a ratio figure R = (A/B).
(i) Figure A (input)
The Input (figure A) is reported as follows:
Energy:
(a) |
Total annual energy consumption, expressed in MWh or GJ; |
(b) |
Percentage of (a) from renewable energy sources, produced by the organisation. |
The indicator (b) captures the percentage of annual energy consumption from renewable energy sources actually produced by the organisation. Energy purchased from an energy provider is not included under this indicator, and may be considered as part of ‘green procurement’ measures.
Materials:
Annual mass flow of different materials used, expressed in tonnes, excluding energy carriers and water.
The annual mass flow of different materials can be divided according to the use to which they are put. They might, for instance, include raw materials such as metal, wood or chemicals, or intermediate goods, depending on the activities of the organisation.
Water:
Total annual water consumption, expressed in m3.
This indicator requires reporting on the total annual amount of water the organisation consumes.
It is useful to clarify different types of water consumption, and to report on consumption according to the source of the water, e.g. surface water, ground water.
Other useful information might include the amount of waste water, waste water treated and reused, rainwater and grey-water recycling.
Waste:
This covers the total annual generation of
— |
waste (broken down by type) expressed in tonnes; |
— |
hazardous waste, expressed in tonnes or kilograms. |
Reporting on waste and hazardous waste is compulsory under the EMAS Regulation. It is good practice to break waste down by type for both streams. The results of the environmental review, including relevant legal obligations on reporting waste, should be taken as a basis. More detailed reporting could be done in line with the national waste classification system which implements the European List of Waste.
Reporting long lists of waste types could be counterproductive and confusing for communication purposes, so ‘clustering’ information according to the European List is an option. Waste could then be recorded by weight or volume for the different types, such as metals, plastic, paper, sludge, ash, etc. Adding information on the amount of waste that is recovered, recycled, used for energy production or landfilled, could also be useful.
Land use with regard to biodiversity:
Use of land, expressed in m2 of built-up-area.
Biodiversity is a complex, relatively new issue among core indicators. Some of the factors driving loss of biodiversity (climate change, emission/pollution) are already covered by environmental aspects and related indicators in the EMAS Regulation, covering energy and water consumption, emissions, waste, etc.
Not all biodiversity indicators are relevant for all sectors/organisations, and not all can be implemented directly when starting to manage these aspects. The environmental review should give a good indication of relevant factors. The organisation should consider not just local impacts, but also direct and indirect impacts on biodiversity more widely, e.g. extraction of raw material, procurement/supply chain, production and product, transport and logistics, marketing and communication. There is no single indicator relevant for all organisations.
The biodiversity indicator on land use, provided for in Annex IV of the EMAS Regulation, can be seen as common denominator. This only covers the premises of the organisation in terms of built-up area. However, it is highly recommended that sealed areas should also be included in the land use indicator.
Emissions:
(a) |
Total annual emissions of greenhouse gases (CO2, CH4, N2O, HFC, PFC, SF6), expressed in tonnes of CO2 equivalent; |
(b) |
Total annual air emissions (including at least SO2, NOx, PM), expressed in kilograms or tonnes. Note: Because the impacts of these substances are different, they should not be added up. |
The approach to quantifying emissions, especially greenhouse gases and air pollutants, needs to be clarified (21). As a starting point, organisations need to take into account existing legal requirements. This is clearly the case for organisations whose installations fall under the scope of the EU Emission Trading Scheme or the European Pollutant Release and Transfer Register Regulation. In other cases, European, globally recognised or national/regional common methodologies when available may be applied.
Although reporting on core indicators is only mandatory for direct aspects, an organisation has to take into account all significant environmental aspects, direct and indirect. So it is best to report significant indirect greenhouse gas emissions, preferably separately from direct emissions.
(ii) Figure B (output)
Overall annual output (figure B) is the same for all fields, but adapted for different types of organisation:
(a) |
Production sector (industry): state the total gross value-added, expressed in million euro or total annual physical output, expressed in tonnes. Small organisations can state the total annual turnover or number of employees; |
(b) |
Non-production sector (service, administration): state the number of employees. |
2.3.2.2. Core indicators and related elements of flexibility — rationale
It is important to understand the rationale behind the setting of indicators and the elements of flexibility provided in the EMAS Regulation (Annex IV of the EMAS Regulation).
Annex IV C.1 states that indicators must:
(a) |
give an accurate appraisal of the organisation's environmental performance; |
(b) |
be understandable and unambiguous; |
(c) |
allow for a year on year comparison to assess the development of the environmental performance of the organisation; |
(d) |
allow for comparison with sector, national or regional benchmarks as appropriate; |
(e) |
allow for comparison with regulatory requirements as appropriate. |
Those are the main functions of the key performance indicators.
However, there is some flexibility over use of the indicators if that helps to achieve their function.
They are as follows:
— |
Conditions for using the confidentiality clause, referred in Annex IV C.1 — ‘if disclosure would adversely affect the confidentiality of commercial or industrial information (…), the organisation may be permitted to index this information in its reporting, e.g., by establishing a base line year (with the index number 100) from which the development of the actual input/impact would appear.’ This clause could be invoked if the use of an indicator might disclose sensitive data that could enable a competitor to calculate the average price of production; |
— |
Conditions for NOT reporting on a specific core indicator provided in Annex IV — Annex IV C2(a) and (b) on core indicators states that ‘where an organisation concludes that one or more core indicators are not relevant to its significant direct environmental aspects, that organisation may not report on those core indicators. The organisation shall provide justification to that effect with reference to its environmental review.’ For the sake of transparency, that justification should also be mentioned in the environmental statement. Since each core indicator is composed of a figure A for input, B for output and R for the ratio A/B, this element of flexibility applies for the entire core indicator as such, including the specific relation A/B; |
— |
Conditions for reporting using another indicator (A/B) INSTEAD OF a specific core indicator as in Annex IV — if an organisation decides not to report under (a) specific indicator(s) as provided for in Annex IV, but chooses another instead, that indicator also has to provide for an input A and an output B. Using this flexibility should always be justified with reference to the environmental review, showing how the option chosen helps to better indicate the relevant performance. For this specific provision, the EMAS Sectoral Reference Document should be taken into account, if available for the sector under consideration. For example, instead of ‘number of employees’, a tourist accommodation service may opt for ‘number of guest-nights’, a school may choose ‘number of pupils’, a waste management organisation may use ‘amount of waste managed, in tons’, and a hospital may prefer ‘number of overnight patients’, etc.; |
— |
Conditions for using other elements to express input (A) and output (B), IN ADDITION to the specific core indicators provided in Annex IV — An organisation may also use other elements to express the total annual input/impact in a given field and the overall annual output. For example, a service organisation may report using a measure of output (B) ‘number of employees’ for its administrative component and a different measure of output for the specific service provided; |
— |
Measurement units — If those cited in Annex IV of the EMAS Regulation do not clearly reflect the environmental performance of an organisation and do not provide a clear picture for communication purposes, then alternatives may be used, as long as the organisation justifies this. It must be possible to convert the units into those specified in the Regulation. Ideally, a footnote with a conversion should be added; |
— |
Currencies related to GVA or total annual turnover other than Euros — Though the EMAS Regulation refers to ‘million Euros’ as a measure of output for gross value-added, organisations based in countries that do not belong to the Eurozone can use their national currency. |
2.3.2.3. Other relevant environmental performance indicators
The organisation must also report on its performance according to other relevant indicators related to significant environmental aspects mentioned in the environmental review.
Where sectoral reference documents (SRDs) as referred to in Article 46 of the EMAS Regulation are available for the specific sector, the assessment of the organisation's environmental performance shall take into account the relevant document.
Organisations should therefore consider the relevant sector-specific environmental performance indicators in the SRD when choosing the indicators (22) to use for their reporting of environmental performance. They should take into account the indicators proposed in the corresponding SRD and their relevance with regards to the significant environmental aspects identified by the organisation in its environmental review. Indicators should only be taken into account where relevant to those environmental aspects that are judged as being most significant in the environmental review.
2.3.2.4. Local accountability
Local accountability is important in EMAS. That is why all EMAS registered organisations should report on the significant environmental impacts of each site as described in the Annex IV of the Regulation.
In any case, information on trends in emissions to air and water, water consumption, use of energy and the amount of waste should be provided at site level. When the multisite verification procedure described in Section 2.4.3 of this User Guide applies, such information can be provided at the level of groups of sites provided that those figures reflect accurately the trends at site level.
The organisation may index information only if there are confidentiality issues (see 2.3.2.2)
Furthermore, the fact that ongoing improvements can be achieved on permanent sites, but not on temporary sites needs to be taken into account. If this issue arises, it should be stated in the environmental review. The possibility of implementing alternative measures, including, for instance, other ‘soft’ (qualitative) indicators, should be taken into account. In any case, for sectors covered by EMAS sectoral reference documents, information concerning temporary sites may be considered.
Table 7
Example of the use of core performance indicators in public administration organisations
Core indicator |
Annual input/impact (A) |
Overall annual output of the organisation (B) |
Ratio A/B |
Energy |
Annual consumption MWh, GJ |
Number of employees (non-production sector) |
MWh/person and/or KWh/person |
Materials |
Annual consumption of paper in tonnes |
Number of employees (non-production sector) |
Tonnes/person and/or Number of paper sheets/person/day |
Water |
Annual consumption m3 |
Number of employees (non-production sector) |
m3/person and/or l/person |
Waste |
Annual generation of waste in tonnes |
Number of employees (non-production sector) |
Tonnes of waste/person and/or Kg/person |
Annual generation of hazardous waste in kilograms |
Kg of hazardous waste/person |
||
Land use with regard to biodiversity |
Use of land, m2 of built-up area (including sealed area) |
Number of employees (non-production sector) |
m2 of built-up area/person and/or m2 of sealed area/person |
GHG emissions |
Annual emissions of GHG in tonnes of CO2e (CO2e = CO2 equivalent) |
Number of employees (non-production sector) |
tonnes CO2e/person and/or Kg CO2e/person |
Table 8
Example of the use of core performance indicators in the production sector
Core indicator |
Annual input/impact (A) |
Overall annual output of the organisation (B) |
Ratio A/B |
Energy |
Annual consumption MWh, GJ |
Total annual gross value added (million euros) (*1) or Total annual physical output (tonnes) |
MWh/million euro or MWh/tonne of product |
Materials |
Annual mass flow of the different materials used, in tonnes |
Total annual gross value added (million euros) (*1) or Total annual physical output (tonnes) |
For each one of the different materials used: Material in tonnes/million euro or Material in tonnes/tonne product |
Water |
Annual consumption m3 |
Total annual gross value added (million euros) (*1) or Total annual physical output (tonnes) |
m3/million euro or m3/tonne of product |
Waste |
Annual generation of waste in tonnes |
Total annual gross value added (million euros) (*1) or Total annual physical output (tonnes) |
Tonnes of waste/million euro or Tonnes of waste/tonne product |
Annual generation of hazardous waste in tonnes |
Tonnes of hazardous waste/million euro or Tonnes of hazardous waste/tonne product |
||
Land use with regard to biodiversity |
Use of land, m2 of built-up area (including sealed area) |
Total annual gross value added (million euros) (*1) or Total annual physical output (tonnes) |
m2 of built-up area and/or m2 of sealed area/million euro or m2 of built-up area and/or m2 of sealed area/tonne of product |
GHG emissions |
Annual emissions of GHG in tonnes of CO2e |
Total annual gross value added (million euros) (*1) or Total annual physical output (tonnes) |
Tonnes of CO2 equivalent/million euro or Tonnes of CO2 equivalent/tonne of product |
Note: The EMAS environmental statement can be used to report on specific core performance indicators, in particular energy and greenhouse gases emissions. |
2.4. VERIFICATION AND VALIDATION PROCEDURE
‘ “Verification” means the conformity assessment process carried out by an environmental verifier to demonstrate whether an organisation's environmental review, environmental policy, environmental management system and internal audit and its implementation fulfil the requirements of this Regulation.’
‘ “Validation” means the confirmation by the environmental verifier who carried out the verification, that the information and data in an organisation's environmental statement and updated environmental statement are reliable, credible and correct and meet the requirements of the Regulation.’
2.4.1. Who is allowed to verify and validate EMAS?
Only accredited or licensed environmental verifiers can carry out these tasks.
‘ “Environmental verifier” means: a conformity assessment body as defined in Regulation (EC) No 765/2008 [of the European Parliament and of the Council] (23) or any association or group of such bodies, which has obtained accreditation in accordance with this Regulation; or any natural or legal person, or any association or group of such persons, which has obtained a licence to carry out verification and validation in accordance with this Regulation.’ (24)
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The organisation may contact the EMAS Competent Body in its Member State, or the EMAS Accreditation or Licensing Body responsible for the accreditation of EMAS verifiers for information about accredited environmental verifiers. If an organisation wants information about verifiers operating in their sector from Member States other than their own, this is available through the EU EMAS register (25); |
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The scope of an accredited or licensed environmental verifier is determined according to NACE codes, classification of economic activities set out in Regulation (EC) No 1893/2006 of the European Parliament and of the Council (26). When an organisation contracts an environmental verifier, it must ensure the verifier is accredited or licensed for the specific NACE code corresponding to the organisation's activities; |
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Once the verifier is accredited or licensed in one Member State, he/she can operate in all EU countries (27); |
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Information about accredited or licensed verifiers is available either from the Commission EMAS website or through the appropriate bodies in Member States. |
Note: It is useful for the organisation to check whether the verifier has notified the information mentioned in Article 24 of the EMAS Regulation to the relevant accreditation or licensing body at least four weeks before verification to allow supervision by Accreditation or Licensing Body of the Member State where they wish to operate. In absence of supervision the Competent Body may refuse the registration of the organisation.
2.4.2. What are the tasks of environmental verifiers?
(1) |
Verify if the organisation is in conformity with all the requirements of the EMAS Regulation with respect to the initial environmental review, environmental management system, environmental audit and its results and the environmental statement; |
(2) |
Check if the organisation complies with relevant Community, national, regional and local legal requirements relating to the environment; Note 1: The verifier has to check if the organisation has established implemented and maintained procedure(s) for periodically evaluating compliance with applicable legal requirements (28). The verifier carries out an in-depth check of the legal compliance of a company. Part of this task is checking material evidence received that there is no breach of environmental legislation (29). Verifiers may use the findings of enforcement authorities. If they do not find evidence of non-compliance, this is stated in the environmental declaration and signed by the verifier. However, the duty of the verifier is to check that the requirements of the Regulation are satisfied through the usual audit techniques. This means that s/he will not be able to check compliance with legal requirements in the same way as enforcement authorities do. Note 2: If a verifier detects a case of non-conformity or non-compliance in the period between two registrations, the following options exist. He/she can report to the Competent Body that the organisation in question has to be deleted from the EMAS Register. Alternatively if the organisation has shown that it took timely measures in cooperation with the enforcement authorities to restore legal compliance, the verifier can still sign the declaration on verification and validation activities, as per Annex VII of the Regulation. |
(3) |
Check the organisation's continuous improvement of environmental performance; |
(4) |
Check the reliability, credibility and accuracy of the data included and used in the EMAS environmental statement and any environmental information to be validated; |