Avis juridique important

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31999L0013

Council Directive 1999/13/EC of 11 March 1999 on the limitation of emissions of volatile organic compounds due to the use of organic solvents in certain activities and installations

Official Journal L 085 , 29/03/1999 P. 0001 - 0022

COUNCIL DIRECTIVE 1999/13/EC of 11 March 1999 on the limitation of emissions of volatile organic compounds due to the use of organic solvents in certain activities and installationsTHE COUNCIL OF THE EUROPEAN UNION,Having regard to the Treaty establishing the European Community, and in particular Article 130s(1) thereof,Having regard to the proposal from the Commission (1),Having regard to the opinion of the Economic and Social Committee (2),Acting in accordance with the procedure laid down in Article 189c of the Treaty (3),(1) Whereas the European Community action programme on the environment approved by the Council and the representatives of the Governments of the Member States meeting within the Council by resolutions of 22 November 1973 (4), 17 May 1977 (5), 7 February 1983 (6), 19 October 1987 (7) and 1 February 1993 (8) stresses the importance of the prevention and reduction of air pollution;(2) Whereas in particular the resolution of 19 October 1987 emphasises the importance of Community action to concentrate, inter alia, on implementation of appropriate standards in order to ensure a high level of public health and environmental protection;(3) Whereas the European Community and its Member States are parties to the Protocol to the 1979 Convention on Long-Range Transboundary Air Pollution concerning the control of emissions of volatile organic compounds in order to reduce their transboundary fluxes and the fluxes of the resulting secondary photochemical oxidant products so as to protect human health and the environment from adverse effects;(4) Whereas pollution due to volatile organic compounds in one Member State often influences the air and water of other Member States; whereas, in accordance with Article 130r of the Treaty, action at Community level is necessary;(5) Whereas, because of their characteristics, the use of organic solvents in certain activities and installations gives rise to emissions of organic compounds into the air which can be harmful for public health and/or contributes to the local and transboundary formation of photochemical oxidants in the boundary layer of the troposphere which cause damage to natural resources of vital environmental and economic importance and, under certain exposure conditions, has harmful effects on human health;(6) Whereas the high incidence of high tropospheric ozone concentrations in recent years has triggered widespread concern regarding the impact on public health and the environment;(7) Whereas, therefore, preventive action is required to protect public health and the environment against the consequences of particularly harmful emissions from the use of organic solvents and to guarantee citizens the right to a clean and healthy environment;(8) Whereas emissions of organic compounds can be avoided or reduced in many activities and installations because potentially less harmful substitutes are available or will become available within the coming years; whereas, where appropriate substitutes are not available, other technical measures should be taken to reduce emissions into the environment as much as economically and technically feasible;(9) Whereas the use of organic solvents and the emissions of organic compounds which have the most serious effects on public health should be reduced as much as technically feasible;(10) Whereas installations and processes which fall under this Directive should at least be registered if they are not subject to authorisation under Community or national legislation;(11) Whereas existing installations and activities should, where appropriate, be adapted so that within an appropriate period they meet the requirements established for new installations and activities; whereas that period should be consistent with the timetable for compliance of Council Directive 96/61/EC of 24 September 1996 concerning integrated pollution prevention and control (9);(12) Whereas the relevant parts of existing installations which undergo substantial change must, as a matter of principle, meet the new installation standards for the substantially changed equipment;(13) Whereas organic solvents are used by many different types of installations and activities so that, in addition to general requirements, specific requirements should be defined and, at the same time, thresholds for the size of the installations or activities which have to comply with this Directive;(14) Whereas a high level of environmental protection requires the setting and achievement of emission limits for organic compounds and appropriate operating conditions, in accordance with the principle of best available techniques, for certain installations and activities using organic solvents within the Community;(15) Whereas in some cases Member States may exempt operators from complying with the emission limit values because other measures, such as the use of low-solvent or solvent-free products or techniques, provide alternative means of achieving equivalent emission reductions;(16) Whereas emission-limiting measures adopted before the entry into force of this Directive should be taken into account in an appropriate way;(17) Whereas alternative approaches to reduction may allow the objectives of this Directive to be achieved more effectively than by implementing uniform emission limit values; whereas, therefore, Member States may exempt existing installations from compliance with the emission limits if they implement a national plan, which will, within the timetable for implementation of this Directive, lead to an at least equal reduction in emissions of organic compounds from these activities and installations;(18) Whereas existing installations falling under Directive 96/61/EC which are covered by a national plan can under no circumstances be exempted from the provisions of that Directive, including Article 9(4) thereof;(19) Whereas in many cases small and medium-sized, new and existing installations may be allowed to comply with somewhat less stringent requirements to maintain their competitiveness;(20) Whereas for dry cleaning a zero threshold is appropriate, subject to specified exemptions;(21) Whereas monitoring of emissions is required, including the application of measurement techniques, to assess the mass concentrations or the quantity of the pollutants whose release into the environment is permitted;(22) Whereas operators should reduce emissions of organic solvents, including fugitive emissions, and of organic compounds; whereas a solvent management plan is an important tool to verify this; whereas, although guidance may be given, the solvent management plan is not developed to the stage where a Community methodology can be established;(23) Whereas Member States have to establish a procedure to be followed and measures to be taken where emission limitations are exceeded;(24) Whereas the Commission and the Member States should collaborate in order to ensure that information on the implementation of this Directive and on the progress of substitution options is exchanged,HAS ADOPTED THIS DIRECTIVE:Article 1 Purpose and scopeThe purpose of this Directive is to prevent or reduce the direct and indirect effects of emissions of volatile organic compounds into the environment, mainly into air, and the potential risks to human health, by providing measures and procedures to be implemented for the activities defined in Annex I, in so far as they are operated above the solvent consumption thresholds listed in Annex IIA.Article 2 DefinitionsFor the purposes of this Directive:1. installation shall mean a stationary technical unit where one or more activities falling within the scope defined in Article 1 are carried out, and any other directly associated activities which have a technical connection with the activities carried out on that site and which could have an effect on emissions;2. existing installation shall mean an installation in operation or, in accordance with legislation existing before the date on which this Directive is brought into effect, an installation which is authorised or registered or, in the view of the competent authority, the subject of a full request for authorisation, provided that the installation is put into operation no later than one year after the date on which this Directive is brought into effect;3. small installation shall mean an installation which falls within the lower threshold band of items 1, 3, 4, 5, 8, 10, 13, 16 or 17 of Annex IIA or for the other activities of Annex IIA which have a solvent consumption of less than 10 tonnes/year;4. substantial change- for an installation falling within the scope of Directive 96/61/EC, shall have the definition specified in that Directive,- for a small installation, shall mean a change of the nominal capacity leading to an increase of emissions of volatile organic compounds of more than 25 %. Any change that may have, in the opinion of the competent authority, significant negative effects on human health or the environment is also a substantial change,- for all other installations, shall mean a change of the nominal capacity leading to an increase of emissions of volatile organic compounds of more than 10 %. Any change that may have, in the opinion of the competent authority, significant negative effects on human health or the environment is also a substantial change;5. competent authority shall mean the authority or authorities or bodies responsible under the legal provisions of the Member States for carrying out the obligations arising from this Directive;6. operator shall mean any natural or legal person who operates or controls the installation or, where this is provided for in national legislation, to whom decisive economic power over the technical functioning of the installation has been delegated;7. authorisation shall mean a written decision by which the competent authority grants permission to operate all or part of an installation;8. registration shall mean a procedure, specified in a legal act, involving at least notification to the competent authority by the operator of the intention to operate an installation or activity falling within the scope of this Directive;9. emission shall mean any discharge of volatile organic compounds from an installation into the environment;10. fugitive emissions shall mean any emissions not in waste gases of volatile organic compounds into air, soil and water as well as, unless otherwise stated in Annex IIA, solvents contained in any products. They include uncaptured emissions released to the outside environment via windows, doors, vents and similar openings;11. waste gases shall mean the final gaseous discharge containing volatile organic compounds or other pollutants, from a stack or abatement equipment into air. The volumetric flow rates shall be expressed in m³/h at standard conditions;12. total emissions shall mean the sum of fugitive emissions and emissions in waste gases;13. emission limit value shall mean the mass of volatile organic compounds, expressed in terms of certain specific parameters, concentration, percentage and/or level of an emission, calculated at standard conditions, N, which may not be exceeded during one or more periods of time;14. substances shall mean any chemical element and its compounds, as they occur in the natural state or as produced by industry, whether in solid or liquid or gaseous form;15. preparation shall mean mixtures or solutions composed of two or more substances;16. organic compound shall mean any compound containing at least the element carbon and one or more of hydrogen, halogens, oxygen, sulphur, phosphorus, silicon or nitrogen, with the exception of carbon oxides and inorganic carbonates and bicarbonates;17. volatile organic compound (VOC) shall mean any organic compound having at 293,15 K a vapour pressure of 0,01 kPa or more, or having a corresponding volatility under the particular conditions of use. For the purpose of this Directive, the fraction of creosote which exceeds this value of vapour pressure at 293,15 K shall be considered as a VOC;18. organic solvent shall mean any VOC which is used alone or in combination with other agents, and without undergoing a chemical change, to dissolve raw materials, products or waste materials, or is used as a cleaning agent to dissolve contaminants, or as a dissolver, or as a dispersion medium, or as a viscosity adjuster, or as a surface tension adjuster, or a plasticiser, or as a preservative;19. halogenated organic solvent shall mean an organic solvent which contains at least one atom of bromine, chlorine, fluorine or iodine per molecule;20. coating shall mean any preparation, including all the organic solvents or preparations containing organic solvents necessary for its proper application, which is used to provide a decorative, protective or other functional effect on a surface;21. adhesive shall mean any preparation, including all the organic solvents or preparations containing organic solvents necessary for its proper application, which is used to adhere separate parts of a product;22. ink shall mean a preparation, including all the organic solvents or preparations containing organic solvents necessary for its proper application, which is used in a printing activity to impress text or images on to a surface;23. varnish shall mean a transparent coating;24. consumption shall mean the total input of organic solvents into an installation per calendar year, or any other 12-month period, less any VOCs that are recovered for reuse;25. input shall mean the quantity of organic solvents and their quantity in preparations used when carrying out an activity, including the solvents recycled inside and outside the installation, and which are counted every time they are used to carry out the activity;26. reuse of organic solvents shall mean the use of organic solvents recovered from an installation for any technical or commercial purpose and including use as a fuel but excluding the final disposal of such recovered organic solvent as waste;27. mass flow shall mean the quantity of VOCs released, in unit of mass/hour;28. nominal capacity shall mean the maximum mass input of organic solvents by an installation averaged over one day, if the installation is operated under conditions of normal operation at its design output;29. normal operation shall mean all periods of operation of an installation or activity except start-up and shut-down operations and maintenance of equipment;30. contained conditions shall mean conditions under which an installation is operated such that the VOCs released from the activity are collected and discharged in a controlled way either via a stack or abatement equipment and are therefore not entirely fugitive;31. standard conditions shall mean a temperature of 273,15 K and a pressure of 101,3 kPa;32. average over 24 hours shall mean the arithmetic average of all valid readings taken during the 24-hour period of normal operation;33. start-up and shut-down operations shall mean operations whilst bringing an activity, an equipment item or a tank into or out of service or into or out of an idling state. Regularly oscillating activity phases are not to be considered as start-ups and shut-downs.Article 3 Obligations applying to new installationsMember States shall adopt the necessary measures to ensure that:1. all new installations comply with Articles 5, 8 and 9;2. all new installations not covered by Directive 96/61/EC are registered or undergo authorisation before being put into operation.Article 4 Obligations applying to existing installationsWithout prejudice to Directive 96/61/EC, Member States shall adopt the necessary measures to ensure that:1. existing installations comply with Articles 5, 8 and 9 no later than 31 October 2007;2. all existing installations must have been registered or authorised by 31 October 2007 at the latest;3. those installations to be authorised or registered using the reduction scheme of Annex IIB notify this to the competent authorities by 31 October 2005 at the latest;4. where an installation:- undergoes a substantial change, or- comes within the scope of this Directive for the first time following a substantial change,that part of the installation which undergoes the substantial change shall be treated either as a new installation or as an existing installation, provided that the total emissions of the whole installation do not exceed those that would have resulted had the substantially changed part been treated as a new installation.Article 5 Requirements1. Member States shall take the appropriate measures, either by specification in the conditions of the authorisation or by general binding rules to ensure that paragraphs 2 to 12 are complied with.2. All installations shall comply with:(a) either the emission limit values in waste gases and the fugitive emission values, or the total emission limit values, and other requirements laid down in Annex IIA;or(b) the requirements of the reduction scheme specified in Annex IIB.3. (a) For fugitive emissions, Member States shall apply fugitive emission values to installations as an emission limit value. However, where it is demonstrated to the satisfaction of the competent authority that for an individual installation this value is not technically and economically feasible, the competent authority can make an exception for such an individual installation provided that significant risks to human health or the environment are not to be expected. For each derogation, the operator must demonstrate to the satisfaction of the competent authority that the best available technique is being used;(b) activities which cannot be operated under contained conditions may be exempted from the controls of Annex IIA, when this possibility is explicitly mentioned in that Annex. The reduction scheme of Annex IIB is then to be used, unless it is demonstrated to the satisfaction of the competent authority that this option is not technically and economically feasible. In this case, the operator must demonstrate to the satisfaction of the competent authority that the best available technique is being used.Member States shall report to the Commission on the derogation concerning paragraphs (a) and (b) in accordance with Article 11.4. For installations not using the reduction scheme, any abatement equipment installed after the date on which this Directive is brought into effect shall meet all the requirements of Annex IIA.5. Installations where two or more activities are carried out, each of which exceeds the thresholds in Annex IIA shall:(a) as regards the substances specified in paragraphs 6, 7 and 8, meet the requirements of those paragraphs for each activity individually;(b) as regards all other substances, either:(i) meet the requirements of paragraph 2 for each activity individually; or(ii) have total emissions not exceeding those that would have resulted had point (i) been applied.6. Substances or preparations which, because of their content of VOCs classified as carcinogens, mutagens, or toxic to reproduction under Directive 67/548/EEC (10), are assigned or need to carry the risk phrases R45, R46, R49, R60, R61, shall be replaced, as far as possible and by taking into account the guidance as mentioned in Article 7(1), by less harmful substances or preparations within the shortest possible time.7. For discharges of the VOCs referred to in paragraph 6, where the mass flow of the sum of the compounds causing the labelling referred to in that paragraph is greater than, or equal to, 10 g/h, an emission limit value of 2 mg/Nm³ shall be complied with. The emission limit value refers to the mass sum of the individual compounds.8. For discharges of halogenated VOCs which are assigned the risk phrase R40, where the mass flow of the sum of the compounds causing the labelling R40 is greater than, or equal to, 100 g/h, an emission limit value of 20 mg/Nm³ shall be complied with. The emission limit value refers to the mass sum of the individual compounds.The discharge of VOCs referred to in paragraphs 6 and 8 shall be controlled as emissions from an installation under contained conditions as far as technically and economically feasible to safeguard public health and the environment.9. Discharges of those VOCs which, after the entry into force of this Directive, are assigned or need to carry one of the risk phrases mentioned in paragraphs 6 and 8, shall have to comply with the emission limit values mentioned in paragraphs 7 and 8 respectively, within the shortest possible time.10. All appropriate precautions shall be taken to minimise emissions during start-up and shut-down.11. Existing installations which operate existing abatement equipment and comply with the following emission limit values:- 50 mg C/Nm³ in the case of incineration,- 150 mg C/Nm³ in the case of any other abatement equipment,shall be exempt from the waste gases emission limit values in the table in Annex IIA for a period of 12 years after the date referred to in Article 15, provided the total emissions of the whole installation do not exceed those that would have resulted had all the requirements of the table been met.12. Neither the reduction scheme nor the application of paragraph 11 nor Article 6 exempt installations discharging substances specified in paragraphs 6, 7 and 8 from fulfilling the requirements of those paragraphs.13. Where a risk assessment is carried out in accordance with Council Regulation (EEC) No 793/93 (11) and Commission Regulation (EC) No 1488/94 (12) or Council Directive 67/548/EEC and Commission Directive 93/67/EEC (13) of any of the substances causing the labelling R40, R60 or R61 which are controlled under this Directive, the Commission shall consider the conclusions of the risk assessment and shall take the necessary measures as appropriate.Article 6 National plans1. Without prejudice to Directive 96/61/EC, Member States may define and implement national plans for reducing emissions from the activities and industrial installations covered by Article 1, excluding activities 4 and 11 of Annex IIA. None of the other activities may be excluded from the scope of this Directive by means of a national plan. These plans shall result in a reduction of the annual emissions of VOCs from existing installations covered by this Directive by at least the same amount and within the same time frame as would have been achieved by applying the emission limits under Article 5(2) and (3) and Annex II, during the validity period of the national plan. The national plan, if necessary updated, will be resubmitted to the Commission every three years.A Member State which defines and implements national plans may exempt existing installations from implementation of the emission limit values laid down in Article 5(2) and (3) and Annex II. A national plan may under no circumstances exempt an existing installation from the provisions laid down in Directive 96/61/EC.2. A national plan shall include a list of the measures taken or to be taken to ensure that the aim specified in paragraph 1 will be achieved, including details of the proposed plan monitoring mechanism. It shall also include binding interim reduction targets against which progress towards the aim can be measured. It shall be compatible with the relevant existing Community legislation, including the relevant provisions of this Directive, and shall include:- an identification of the activity or activities to which the plan applies,- the reduction in emissions to be achieved by those activities which corresponds to that which would have been achieved by applying the emission limits as specified in paragraph 1,- the number of installations affected by the plan and their total emissions and the total emission of each of the activities.The plan shall also include a full description of the range of instruments through which its requirements will be achieved, evidence that these instruments will be enforceable and details of the means by which compliance with the plan will be demonstrated.3. The Member State shall submit the plan to the Commission. The plan must be accompanied by supporting documentation sufficient to verify that the aim of paragraph 1 will be achieved, including any documentation specifically requested by the Commission. Existing installations undergoing a substantial change shall remain within the scope of the national plan, provided that they were part of this plan before undergoing such substantial change.4. The Member State shall designate a national authority for the collection and evaluation of the information required by paragraph 3 and for the implementation of the national plan.5. (a) The Commission shall inform the committee referred to in Article 13 of the criteria for assessing national plans, one year after the entry into force of this Directive at the latest.(b) If the Commission, in considering the plan, the resubmitted plan, or in considering the progress reports submitted by the Member State under Article 11, is not satisfied that the objectives of the plan will be achieved within the prescribed period, it shall inform the Member State and the committee referred to in Article 13 of its opinion and of the reasons for reaching such an opinion. It shall do so within six months of receipt of the plan or report. The Member State shall then notify the Commission and inform the committee, within three months, of the corrective measures it will take in order to ensure that the objectives are achieved.6. If the Commission decides within six months of the notification of the corrective measures that those measures are insufficient to ensure that the objective of the plan is achieved within the prescribed period, the Member State shall be obliged to satisfy the requirements of Article 5(2) and (3) and Annex II within the period specified in this Directive in the case of existing installations. The Commission shall inform the committee referred to in Article 13 of its decision.Article 7 Substitution1. The Commission shall ensure that an exchange of information between Member States and the activities concerned on the use of organic substances and their potential substitutes takes place. It shall consider the questions of:- fitness for use,- potential effects on human health and occupational exposure in particular;- potential effects on the environment, and- the economic consequences, in particular, the costs and benefits of the options available,with a view to providing guidance on the use of substances and techniques which have the least potential effects on air, water, soil, ecosystems and human health. Following the exchange of information, the Commission shall publish guidance for each activity.2. Member States shall ensure that the guidance referred to in paragraph 1 is taken into account during authorisation and during the formulation of general binding rules.Article 8 Monitoring1. Member States shall introduce an obligation for the operator of an installation covered by this Directive to supply the competent authority once a year or on request with data that enables the competent authority to verify compliance with this Directive.2. Member States shall ensure that channels to which abatement equipment is connected, and which at the final point of discharge emit more than an average of 10 kg/h of total organic carbon, are monitored continuously for compliance.3. In the other cases, Member States shall ensure that either continuous or periodic measurements are carried out. For periodic measurements at least three readings shall be obtained during each measurement exercise.4. Measurements are not required in the case where end-of-pipe abatement equipment is not needed to comply with this Directive.5. The Commission shall organise an exchange of information on the use of solvent management plans in Member States based on the data for the implementation of this Directive in the three years following the date referred to in Article 15.Article 9 Compliance with emission limit values1. Compliance with the following shall be demonstrated to the satisfaction of the competent authority:- emission limit values in waste gases, fugitive emission values and total emission limit values,- the requirements of the reduction scheme under Annex IIB,- the provisions of Article 5(3).Guidance is provided in Annex III on solvent management plans serving to demonstrate compliance with these parameters.Gas volumes may be added to the waste gas for cooling or dilution purposes where technically justified but shall not be considered when determining the mass concentration of the pollutant in the waste gas.2. Following a substantial change, compliance shall be reverified.3. In the case of continuous measurements the emission limit values shall be considered to be complied with if:(a) none of the averages over 24 hours of normal operation exceeds the emission limit values, and(b) none of the hourly averages exceeds the emission limit values by more than a factor of 1,5.4. In the case of periodic measurements the emission limit values shall be considered to be complied with if, in one monitoring exercise:(a) the average of all the readings does not exceed the emission limit values, and(b) none of the hourly averages exceeds the emission limit value by more than a factor of 1,5.5. Compliance with the provisions of Article 5(7) and (8) shall be verified on the basis of the sum of the mass concentrations of the individual volatile organic compounds concerned. For all other cases, compliance shall be verified on the basis of the total mass of organic carbon emitted unless otherwise specified in Annex IIA.Article 10 Non-complianceMember States shall take appropriate measures to ensure that, if it is found that the requirements of this Directive have been breached:(a) the operator informs the competent authority and takes measures to ensure that compliance is restored within the shortest possible time;(b) in cases of non-compliance causing immediate danger to human health and as long as compliance is not restored under the conditions of paragraph (a), operation of the activity is suspended.Article 11 Information systems and reporting1. At intervals of three years, Member States shall send information to the Commission on the implementation of this Directive in the form of a report. The report shall be drawn up on the basis of a questionnaire or outline drafted by the Commission in accordance with the procedure laid down in Article 6 of Directive 91/692/EEC (14). The questionnaire or outline shall be sent to the Member States six months before the start of the period covered by the report. The report shall be made to the Commission within nine months of the end of the three-year period covered by it. Member States shall publish the reports produced at the same time as they are transmitted to the Commission, subject to the restrictions laid down in Article 3(2) and (3) of Directive 90/313/EEC (15). The first report shall cover the period of the first three years after the date referred to in Article 15.2. The information submitted under paragraph 1 shall, in particular, include sufficient representative data to demonstrate that the requirements of Article 5 and as the case may be, the requirements of Article 6 have been complied with.3. The Commission shall draw up a report on the implementation of this Directive on the basis of the data provided by the Member States at the latest five years after the first reports are submitted by the Member States. The Commission shall submit this report to the European Parliament and the Council, accompanied by proposals if necessary.Article 12 Public access to information1. Without prejudice to Directive 90/313/EEC, Member States shall take the necessary measures to ensure that at least applications for authorisation for new installations or for substantial changes of those installations requiring a permit under Directive 96/61/EC are made available for an appropriate period of time to the public, to enable it to comment on them before the competent authority reaches a decision. Without prejudice to Directive 96/61/EC, no obligation to reformat the information for the public is implied.The decision of the competent authority, including at least a copy of the authorisation, and any subsequent updates, must also be made available to the public.The general binding rules applicable for installations and the list of registered and authorised activities shall be made available to the public.2. The results of emission-monitoring as required under the authorisation or registration conditions referred to in Articles 8 and 9 and held by the competent authority must be made available to the public.3. Paragraphs 1 and 2 shall apply, subject to the restrictions regarding grounds for refusal by public authorities to provide information, including commercial and industrial confidentiality, laid down in Article 3(2) and (3) of Directive 90/313/EEC.Article 13 CommitteeThe Commission shall be assisted by a committee of an advisory nature composed of the representatives of the Member States and chaired by the representative of the Commission.The representative of the Commission shall submit to the committee a draft of the measures to be taken. The committee shall deliver its opinion on the draft, within a time limit which the chairman may lay down according to the urgency of the matter, if necessary by taking a vote.The opinion shall be recorded in the minutes; in addition, each Member State shall have the right to ask to have its position recorded in the minutes.The Commission shall take the utmost account of the opinion delivered by the committee. It shall inform the committee of the manner in which its opinion has been taken into account.Article 14 SanctionsMember States shall determine the sanctions applicable to breaches of the national provisions adopted pursuant to this Directive and shall take all necessary measures for their implementation. The sanctions determined must be effective, proportionate and dissuasive. Member States shall notify these provisions to the Commission at the latest by the date mentioned in Article 15, and shall notify any subsequent modification of them as soon as possible.Article 15 Transposition1. Member States shall bring into force the laws, regulations and administrative provisions necessary to comply with this Directive not later than . . . April 2001. They shall forthwith inform the Commission thereof.When Member States adopt these measures, they shall contain a reference to this Directive or shall be accompanied by such a reference on the occasion of their official publication. The methods of making such a reference shall be laid down by the Member States.2. Member States shall communicate to the Commission the text of the main provisions of national law which they adopt in the field covered by this Directive.Article 16 Entry into forceThis Directive shall enter into force on the day of its publication in the Official Journal of the European Communities.Article 17 AddresseesThis Directive is addressed to the Member States.Done at Brussels, 11 March 1999.For the CouncilThe PresidentJ. TRITTIN(1) OJ C 99, 26.3.1997, p. 32.(2) OJ C 287, 22.9.1997, p. 55.(3) Opinion of the European Parliament of 14 January 1998 (OJ C 34, 2.2.1998, p. 75), Council Common Position of 16 June 1998 (OJ C 248, 7.8.1998, p. 1) and Decision of the European Parliament of 21 October 1998 (OJ C 341, 9.11.1998, p. 70).(4) OJ C 112, 20.12.1973, p. 1.(5) OJ C 139, 13.6.1977, p. 1.(6) OJ C 46, 17.2.1983, p. 1.(7) OJ C 328, 7.12.1987, p. 1.(8) OJ C 138, 1.2.1993, p. 1.(9) OJ L 257, 10.10.1996, p. 26.(10) OJ 196, 16.8.1967, p. 1. Directive as last amended by Commission Directive 98/98/EC (OJ L 355, 30.12.1998, p. 1).(11) OJ L 84, 5.4.1993, p. 1.(12) OJ L 161, 29.6.1994, p. 3.(13) OJ L 227, 8.9.1993, p. 9.(14) OJ L 377, 31.12.1991, p. 48.(15) OJ L 158, 23.6.1990, p. 56.ANNEX ISCOPEThis Annex contains the categories of activity referred to in Article 1. When operated above the thresholds listed in Annex IIA, the activities mentioned in this Annex fall within the scope of the Directive. In each case the activity includes the cleaning of the equipment but not the cleaning of products unless specified otherwise.Adhesive coating- Any activity in which an adhesive is applied to a surface, with the exception of adhesive coating and laminating associated with printing activities.Coating activity- Any activity in which a single or multiple application of a continuous film of a coating is applied to:- vehicles as listed below:- new cars, defined as vehicles of category M1 in Directive 70/156/EEC (1), and of category N1 in so far as they are coated at the same installation as M1 vehicles,- truck cabins, defined as the housing for the driver, and all integrated housing for the technical equipment, of vehicles of categories N2 and N3 in Directive 70/156/EEC,- vans and trucks, defined as vehicles of categories N1, N2 and N3 in Directive 70/156/EEC, but not including truck cabins,- buses, defined as vehicles of categories M2 and M3 in Directive 70/156/EEC,- trailers, defined in categories O1, O2, O3 and O4 in Directive 70/156/EEC,- metallic and plastic surfaces including surfaces of airplanes, ships, trains, etc.,- wooden surfaces,- textile, fabric, film and paper surfaces,- leather.It does not include the coating of substrate with metals by electrophoretic and chemical spraying techniques. If the coating activity includes a step in which the same article is printed by whatever technique used, that printing step is considered part of the coating activity. However, printing activities operated as a separate activity are not included, but may be covered by the Directive if the printing activity falls within the scope thereof.Coil coating- Any activity where coiled steel, stainless steel, coated steel, copper alloys or aluminium strip is coated with either a film forming or laminate coating in a continuous process.Dry cleaning- Any industrial or commercial activity using VOCs in an installation to clean garments, furnishing and similar consumer goods with the exception of the manual removal of stains and spots in the textile and clothing industry.Footwear manufacture- Any activity of producing complete footwear or parts thereof.Manufacturing of coating preparations, varnishes, inks and adhesives- The manufacture of the above final products, and of intermediates where carried out at the same site, by mixing of pigments, resins and adhesive materials with organic solvent or other carrier, including dispersion and predispersion activities, viscosity and tint adjustments and operations for filling the final product into its container.Manufacturing of pharmaceutical products- The chemical synthesis, fermentation, extraction, formulation and finishing of pharmaceutical products and where carried out at the same site, the manufacture of intermediate products.Printing- Any reproduction activity of text and/or images in which, with the use of an image carrier, ink is transferred onto whatever type of surface. It includes associated varnishing, coating and laminating techniques. However, only the following sub-processes are subject to the Directive:- flexography - a printing activity using an image carrier of rubber or elastic photopolymers on which the printing areas are above the non-printing areas, using liquid inks which dry through evaporation,- heatset web offset - a web-fed printing activity using an image carrier in which the printing and non-printing area are in the same plane, where web-fed means that the material to be printed is fed to the machine from a reel as distinct from separate sheets. The non-printing area is treated to attract water and thus reject ink. The printing area is treated to receive and transmit ink to the surface to be printed. Evaporation takes place in an oven where hot air is used to heat the printed material,- laminating associated to a printing activity - the adhering together of two or more flexible materials to produce laminates,- publication rotogravure - a rotogravure printing activity used for printing paper for magazines, brochures, catalogues or similar products, using toluene-based inks,- rotogravure - a printing activity using a cylindrical image carrier in which the printing area is below the non-printing area, using liquid inks which dry through evaporation. The recesses are filled with ink and the surplus is cleaned off the non-printing area before the surface to be printed contacts the cylinder and lifts the ink from the recesses,- rotary screen printing - a web-fed printing activity in which the ink is passed onto the surface to be printed by forcing it through a porous image carrier, in which the printing area is open and the non-printing area is sealed off, using liquid inks which dry only through evaporation. Web-fed means that the material to be printed is fed to the machine from a reel as distinct from separate sheets,- varnishing - an activity by which a varnish or an adhesive coating for the purpose of later sealing the packaging material is applied to a flexible material.Rubber conversion- Any activity of mixing, milling, blending, calendering, extrusion and vulcanisation of natural or synthetic rubber and any ancillary operations for converting natural or synthetic rubber into a finished product.Surface cleaning- Any activity except dry cleaning using organic solvents to remove contamination from the surface of material including degreasing. A cleaning activity consisting of more than one step before or after any other activity shall be considered as one surface cleaning activity. This activity does not refer to the cleaning of the equipment but to the cleaning of the surface of products.Vegetable oil and animal fat extraction and vegetable oil refining activities- Any activity to extract vegetable oil from seeds and other vegetable matter, the processing of dry residues to produce animal feed, the purification of fats and vegetable oils derived from seeds, vegetable matter and/or animal matter.Vehicle refinishing- Any industrial or commercial coating activity and associated degreasing activities performing:- the coating of road vehicles as defined in Directive 70/156/EEC, or part of them, carried out as part of vehicle repair, conservation or decoration outside of manufacturing installations, or- the original coating of road vehicles as defined in Directive 70/156/EEC or part of them with refinishing-type materials, where this is carried out away from the original manufacturing line, or- the coating of trailers (including semi-trailers) (category O).Winding wire coating- Any coating activity of metallic conductors used for winding the coils in transformers and motors, etc.Wood impregnation- Any activity giving a loading of preservative in timber.Wood and plastic lamination- Any activity to adhere together wood and/or plastic to produce laminated products.(1) OJ L 42, 23.2.1970, p. 1. Directive as last amended by Directive 97/27/EC (OJ L 233, 25.8.1997, p. 1).ANNEX IIAI. THRESHOLDS AND EMISSION CONTROLS>TABLE>II. THE VEHICLE COATING INDUSTRY The total emission limit values are expressed in terms of grams of solvent emitted in relation to the surface area of product in square metres and in kilograms of solvent emitted in relation to the car body.The surface area of any product dealt with in the table below is defined as follows:- the surface area calculated from the total electrophoretic coating area, and the surface area of any parts that might be added in successive phases of the coating process which are coated with the same coatings as those used for the product in question, or the total surface area of the product coated in the installation.The surface of the electrophoretic coating area is calculated using the formula:>NUM>2 × total weight of product shell>DEN>average thickness of metal sheet × density of metal sheetThis method shall also be applied for other coated parts made out of sheets.Computer aided design or other equivalent methods shall be used to calculate the surface area of the other parts added, or the total surface area coated in the installation.The total emission limit value in the table below refers to all process stages carried out at the same installation from electrophoretic coating, or any other kind of coating process, through to the final wax and polish of topcoating inclusive, as well as solvent used in cleaning of process equipment, including spray booths and other fixed equipment, both during and outside of production time. The total emission limit value is expressed as the mass sum of organic compounds per m² of the total surface area of coated product and as the mass sum of organic compounds per car body.>TABLE>Vehicle coating installations below the solvent consumption thresholds in the table above shall meet the requirements for the vehicle refinishing sector in Annex IIA.ANNEX IIBREDUCTION SCHEME1. PrinciplesThe purpose of the reduction scheme is to allow the operator the possibility to achieve by other means emission reductions, equivalent to those achieved if the emission limit values were to be applied. To that end the operator may use any reduction scheme, specially designed for his installation, provided that in the end an equivalent emission reduction is achieved. Member States shall report according to Article 11 of the Directive to the Commission about the progress in achieving the same emission reduction, including the experience from the application of the reduction scheme.2. Practice In the case of applying coatings, varnishes, adhesives or inks, the following scheme can be used. Where the following method is inappropriate the competent authority may allow an operator to apply any alternative exemption scheme which it is satisfied fulfils the principles outlined here. The design of the scheme takes into account the following facts:(i) where substitutes containing little or no solvent are still under development, a time extension must be given to the operator to implement his emission reduction plans;(ii) the reference point for emission reductions should correspond as closely as possible to the emissions which would have resulted had no reduction action been taken.The following scheme shall operate for installations for which a constant solid content of product can be assumed and used to define the reference point for emission reductions:(i) the operator shall forward an emission reduction plan which includes in particular decreases in the average solvent content of the total input and/or increased efficiency in the use of solids to achieve a reduction of the total emissions from the installation to a given percentage of the annual reference emissions, termed the target emission. This must be done on the following time frame:>TABLE>(ii) The annual reference emission is calculated as follows:(a) The total mass of solids in the quantity of coating and/or ink, varnish or adhesive consumed in a year is determined. Solids are all materials in coatings, inks, varnishes and adhesives that become solid once the water or the volatile organic compounds are evaporated.(b) The annual reference emissions are calculated by multiplying the mass determined in (a) by the appropriate factor listed in the table below. Competent authorities may adjust these factors for individual installations to reflect documented increased efficiency in the use of solids.>TABLE>(c) The target emission is equal to the annual reference emission multiplied by a percentage equal to:- (the fugitive emission value + 15), for installations falling within item 6 and the lower threshold band of items 8 and 10 of Annex IIA,- (the fugitive emission value + 5) for all other installations.(d) Compliance is achieved if the actual solvent emission determined from the solvent management plan is less than or equal to the target emission.ANNEX IIISOLVENT MANAGEMENT PLAN1. Introduction This Annex provides guidance on carrying out a solvent management plan. It identifies the principles to be applied (item 2) and provides a framework for the mass balance (item 3) and an indication of the requirements for verification of compliance (item 4).2. PrinciplesThe solvent management plan serves the following purposes:(i) verification of compliance as specified in Article 9(1);(ii) identification of future reduction options;(iii) enabling of the provision of information on solvent consumption, solvent emissions and compliance with the Directive to the public.3. DefinitionsThe following definitions provide a framework for the mass balance exercise.Inputs of organic solvents (I):I1 The quantity of organic solvents or their quantity in preparations purchased which are used as input into the process in the time frame over which the mass balance is being calculated.I2 The quantity of organic solvents or their quantity in preparations recovered and reused as solvent input into the process. (The recycled solvent is counted every time it is used to carry out the activity.)Outputs of organic solvents (O):O1 Emissions in waste gases.O2 Organic solvents lost in water, if appropriate taking into account waste water treatment when calculating O5.O3 The quantity of organic solvents which remains as contamination or residue in products output from the process.O4 Uncaptured emissions of organic solvents to air. This includes the general ventilation of rooms, where air is released to the outside environment via windows, doors, vents and similar openings.O5 Organic solvents and/or organic compounds lost due to chemical or physical reactions (including for example those which are destroyed, e.g. by incineration or other waste gas or waste water treatments, or captured, e.g. by adsorption, as long as they are not counted under O6, O7 or O8).O6 Organic solvents contained in collected waste.O7 Organic solvents, or organic solvents contained in preparations, which are sold or are intended to be sold as a commercially valuable product.O8 Organic solvents contained in preparations recovered for reuse but not as input into the process, as long as not counted under O7.O9 Organic solvents released in other ways.4. Guidance on use of the solvent management plan for verification of compliance The use made of the solvent management plan will be determined by the particular requirement which is to be verified, as follows:(i) Verification of compliance with the reduction option in Annex IIB, with a total emission limit value expressed in solvent emissions per unit product, or otherwise stated in Annex IIA.(a) For all activities using Annex IIB the solvent management plan should be done annually to determine consumption (C). Consumption can be calculated according to the following equation:C = I1 - O8A parallel exercise should also be undertaken to determine solids used in coating in order to derive the annual reference emission and the target emission each year.(b) For assessing compliance with a total emission limit value expressed in solvent emissions per unit product or otherwise stated in Annex IIA, the solvent management plan should be done annually to determine emissions (E). Emissions can be calculated according to the following equation:E = F + O1where F is the fugitive emission as defined in section (ii)(a). The emission figure should then be divided by the relevant product parameter.(c) For assessing compliance with the requirements of Article 5(5)(b)(ii), the solvent management plan should be done annually to determine total emissions from all activities concerned, and that figure should then be compared with the total emissions that would have resulted had the requirements of Annex II been met for each activity separately.(ii) Determination of fugitive emissions for comparison with fugitive emission values in Annex IIA:(a) MethodologyThe fugitive emission can be calculated according to the following equation:F = I1 - O1 - O5 - O6 - O7 - O8orF = O2 + O3 + O4 + O9This quantity can be determined by direct measurement of the quantities. Alternatively, an equivalent calculation can be made by other means, for instance by using the capture efficiency of the process.The fugitive emission value is expressed as a proportion of the input, which can be calculated according to the following equation:I = I1 + I2(b) FrequencyDetermination of fugitive emissions can be done by a short but comprehensive set of measurements. It need not be done again until the equipment is modified.


Avis juridique important

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31971L0318

Council Directive 71/318/EEC of 26 July 1971 on the approximation of the laws of the Member States relating to gas volume meters

Official Journal L 202 , 06/09/1971 P. 0021 - 0031 Finnish special edition: Chapter 13 Volume 2 P. 0022  Danish special edition: Series I Chapter 1971(III) P. 0651  Swedish special edition: Chapter 13 Volume 2 P. 0022  English special edition: Series I Chapter 1971(III) P. 0729  - 0739 Greek special edition: Chapter 13 Volume 1 P. 0159  Spanish special edition: Chapter 13 Volume 2 P. 0037  Portuguese special edition Chapter 13 Volume 2 P. 0037

COUNCIL DIRECTIVE of 26 July 1971 on the approximation of the laws of the Member States relating to gas volume meters (71/318/EEC)    THE COUNCIL OF THE EUROPEAN COMMUNITIES,  Having regard to the Treaty establishing the European Economic Community, and in particular Article 100 thereof;  Having regard to the proposal from the Commission;  Having regard to the Opinion of the European Parliament1;  Having regard to the Opinion of the Economic and Social Committee2;  Whereas in the Member States the construction and methods of control of gas volume meters are subject to mandatory provisions which differ from one Member State to another and consequently hinder trade in such instruments ; whereas it is therefore necessary to approximate these provisions;  Whereas the Council Directive of 26 July 19713 on the approximation of the laws of the Member States relating to provisions both for measuring instruments and methods of metrological control has laid down the EEC type approval and EEC initial verification procedures ; whereas, in accordance with that Directive, the technical requirements for the design and functioning of gas volume meters should be laid down;  HAS ADOPTED THIS DIRECTIVE:     Article 1 This Directive applies to the following gas volume meters:    1. Volumetric meters:      - meters with deformable walls;           - meters with rotary pistons.                  2. Non-volumetric meters:  - turbine meters.           Article 2 Those meters which may bear EEC marks and symbols are described in the Annex to this Directive. They shall be subject to EEC type approval and shall be submitted to EEC initial verification.    Article 3 No Member State may refuse, prohibit, or restrict the placing on the market or entry into service of gas volume meters bearing the EEC type approval symbol and the EEC initial verification mark.    Article 4 1. Member States shall put into force the laws, regulations and administrative provisions needed in order to comply with this Directive within eighteen months of its notification, and shall forthwith inform the Commission thereof.  2. Member States shall ensure that the texts of the main provisions of national law which they adopt in the field covered by this Directive are communicated to the Commission.    Article 5 This Directive is addressed to the Member States.     Done at Brussels, 26 July 1971.  For the Council  The President  A. MORO   1 OJ No C 65, 5.6.1970, p. 30.  2 OJ No C 131, 29.10.1970, p. 7.  3 OJ No L 202, 6.9.1971, p. 1.    ANNEX CHAPTER I A. DEFINITION OF CERTAIN TERMS USED IN THE ANNEX     1. Range of load  The range of load of a gas meter is bounded by the maximum flow Qmax and the minimum flow Qmin.       2. Cyclic volume of a volumetric meter  "Cyclic volume V of a volumetric meter" means the volume of gas corresponding to a cycle of operation of the meter, that is to say to the whole of the movements of the moving components of the meter at the end of which all these components except the indicator and the intermediate transmissions return, for the first time, to their original position.  It is calculated by multiplying the value of the volume represented by a complete revolution of the test element, by the transmission ratio of the measuring device to the index counter.       3. Operating pressure and reference pressure      3.1. Operating pressure  The operating pressure of a gas meter is the difference between the pressure of the gas at the inlet of the meter and the atmospheric pressure.           3.2. Reference pressure  The reference pressure pr of a gas meter is the gas pressure to which the indicated volume of gas is related.  The pressure tapping for measuring the reference pressure is laid down in Chapter III.                  4. Pressure absorption  The pressure absorption of a gas meter is the difference between the pressures measured at the inlet and outlet of the meter during the flow of a gas.       5. Output drive constant  The constant of an output drive is the value of the volume represented by a complete turn of the shaft of this drive ; this value is calculated by multiplying the value of the volume represented by a complete turn of the test element by the transmission ratio of the index counter to this shaft.         B. GENERAL PROVISIONS FOR GAS VOLUME METERS     1. General      1.1. Chapter I of this Annex lays down the general provisions which must be satisfied by all gas volume meters covered by Article 1 of this Directive.           1.2. Chapters II and III of this Annex lay down the special provisions relating to the meters concerned.                  2. Construction      2.1. Materials  The meters must be manufactured of solid materials with low internal stresses, which change little with age, and which are sufficiently resistant to corrosion and attack by the various gases which are normally distributed or by any of their condensates.            2.2. Soundness of meters  The cases of meters must be gas-tight at the maximum operating pressure.           2.3. Protection against interference  The meters must be so constructed that any interference which could affect the accuracy of measurement is impossible without damaging the verification marks or protective seals.           2.4. Direction of gas flow  For meters whose indicating devices function positively only for one direction of flow, this direction must be indicated by an arrow.  This arrow is not required if the direction of gas flow is fixed by the construction.           2.5. Metrological properties  At a flow equal to Qmax a meter must be able to operate continuously for the time laid down in Chapter II of III without any change in its metrological performance beyond the limits specified in those chapters.                  3. Additional devices      3.1. Meters may be fitted with additional devices (for correction, recording, supplementary indication etc) ; their addition is subject to the EEC type approval procedure.           3.2. Meters may be fitted with output drives to operate a detachable indicator, a pre-payment device, or any other complementary or additional device.        3.2.1. When these controls are not used, the free end of the drive must be protected by a plug or similar arrangement which can be sealed.               3.2.2.  >PIC FILE= "T0038182">                           3.3. Meters may be fitted with integral pulse generators.   >PIC FILE= "T0038183">                   4. Inscriptions      4.1. Each meter must carry, grouped together either on the dial plate of the indicating device or on a special badge plate, the following inscriptions:        (a) the number of the type approval of the meter               (b) the identification mark or name of the manufacturer               (c) the number and year of manufacture of the meter               (d) the size designation of the meter : this has the form of a capital G followed by a number which is laid down in Chapter II and III               (e) the maximum flow expressed as : Qmax =... m3/h               (f) the minimum flow expressed as : Qmin =... m3/h (or dm3/h)               (g) the maximum operating pressure expressed as : Pmax... MN/m2 (or N/m2), or Pmax... bar (or... mbar)               (h) for volumetric meters, the nominal value of the cyclic volume expressed as : V =... m3 (or dm3).  These inscriptions must be directly visible, easily legible, and indelible under the normal conditions of use of the meter.           4.2. The metrological service which issues the type approval may decide the cases in which the nature of the gas must also be specified on the badge plate.           4.3. The meter may also carry the commercial designation, a special series number, the name of the gas distributor, a mark indicating that it conforms to a European standard, and an indication relating to any repairs made. Unless specially authorised, any other indication or inscription is prohibited.                   5. Counter and test element      5.1. Counter        5.1.1. The counters must be in the form of drums ; however, the last element may be excepted from this rule. The drums must be calibrated in cubic metres or decimal multiples or submultiples of the cubic metre. The symbol m3 must be marked on the index plate.          5.1.1.1. The drums indicating the submultiples of the cubic metre if provided must be clearly distinguishable from the other drums, and separated from them by a clearly marked decimal point.                   5.1.1.2. In cases in which the last drum is figured in decimal multiples of a cubic metre, the index plate must be marked with either:            (a) one or more fixed zero's as appropriate after the last drum ; or                       (b) the indication "× 10, × 100, × 1000 etc. " in such a way that the reading is always made in cubic metres.                                                         5.1.2. The counter must have sufficient numbered drums to be able to indicate within one unit of the last drum, the volume passed during an operating period of one thousand hours at maximum flow rate.                          5.2. Test element        5.2.1. Meters must be designed in such a way that checking can be done with sufficient accuracy. For this purpose they must incorporate in their design an integral test unit or arrangements permitting the connection of a portable test unit.               5.2.2. The integral test element may be the last element of the counter in one of the two following forms:          (a) a continuously revolving drum carrying a graduated scale;                   (b) a pointer passing over a fixed dial having a graduated scale or a disc carrying a graduated scale moving past a fixed reference mark.                                  5.2.3. On the graduated scales of these test elements the unit of the graduations must be indicated clearly and unambiguously in m3 or decimal submultiples of the m3 ; the beginning of the scale must be indicated by the figure zero.          5.2.3.1. The interval between scale divisions must be constant throughout the scale and not less than 1 millimetre.                   5.2.3.2. The value of the scale divisions must be in the form 1 × 10n, 2 × 10n, or 5 × 10n m3, n being a whole positive or negative number or zero.                   5.2.3.3. The graduation lines must be fine and uniform. In cases in which the division is of the form 1 × 10n or 2 × 10n m3, all the lines representing multiples of 5, and in the case of a division of the form 5 × 10n m3, all the lines representing multiples of 2, must be distinguished by a greater length.                                  5.2.4. The pointer or the reference mark must be sufficiently thin to permit certain and easy reading.                          5.3. Diameters of drums and dials  The diameters of drums must be at least 16 millimetres.  The diameter of the graduated scales mentioned in Chapter I B 5.2.2. b must be at least 32 millimetres.           5.4. Reading of the counter  The counter must be so designed that it can be read by simple juxtaposition of the figures.           5.5. Advance of figures  The advance by one figure at any part of the index must be completed whilst the figure of the immediately next lower range describes the last tenth of its course.           5.6. Removal of the counter  Meters must be so designed that the counter may be removed easily during examination.                   6. Maximum permissible errors      6.1. The measuring errors are expressed as a relative value by the ratio, as a percentage, of the difference between the volume indicated and the volume actually passed by the meter, to the latter volume.           6.2. These errors relate to the measurement of volumes of air having a reference density of 1 72 kg/m3. Under normal atmospheric conditions the ambient air in a test laboratory may be considered to satisfy this condition.           6.3. The maximum permissible errors are specified in Chapters II and III ; they are valid for the authorised direction of flow.                  7. Pressure absorption      7.1. Maximum permissible values  The maximum permissible values of pressure absorption are specified in Chapters II and III.                  8. Application of verification marks and seals      8.1. Purpose  The application of EEC verification marks and seals on a gas meter certifies solely that the meter meets the requirements of the present Directive.           8.2. Location        8.2.1. The locations of the marks must be chosen in such a way that dismantling of the part sealed will involve destruction of the marks.               8.2.2. When the inscriptions mentioned in item 4.1. of Chapter I B are on a special badge plate, one of the marks should be fixed in such a manner that it is damaged if the special plate is removed.               8.2.3. Locations should be provided for verification marks or sealing:          (a) on all plates carrying an inscription required by the present Annex;                   (b) on all parts of the casing which cannot otherwise be protected against interference liable to affect the accuracy of measurement.                                                    9. EEC Type approval and initial verification      9.1. EEC Type approval        9.1.1 The request for type approval of a meter must include the following documents, accompanying the type submitted:          - a description of the meter for which approval is requested;                   - a drawing in perspective or a photograph of this meter;                   - a plan of the assembly of the complete meter, supplemented if necessary by detailed drawings;                   - a parts list and all other information considered necessary by the metrology services concerned;                   - a plan showing the locations for verification marks and for protective seals;                   - a declaration specifying that the meters manufactured in conformity with the type meet the requirements for safety, particularly those concerning the maximum operating pressure as indicated on the badge plate.                                             9.2. EEC Initial verification        9.2.1. Meters submitted for the EEC initial verification shall be in working order. If the meters are to be used with additional devices operated by output drives, these accessories must have been connected during the examination unless a later connection has been expressly authorised.                                 10. Verification marks and seals  Meters having undergone successfully the verification tests:      - shall be provided with a verification mark;           - shall receive seals in the locations provided for the protection of certain components against interference liable to affect the meter characteristics.                     CHAPTER II PROVISIONS RELATING TO GAS VOLUME METERS WITH DEFORMABLE WALLS     1. Field of application  The present Chapter applies, together with the provisions of Chapter I, to gas meters in which the measurement of gas passed through is effected by means of measuring chambers with deformable walls.       2. Range of capacity and designation      2.1. The following table gives the authorised values for maximum flow, the upper limits of the corresponding minimum flows, and the minimum values of cyclic volumes, corresponding to the designation (G) of the meters: >PIC FILE= "T0038184">            2.2. If for a type of meter the value of Qmin is lower than the number given in the table of item 2.1 of this Chapter, the numerical value of this Qmin must be expressed by a number in column 3 of this table or by a decimal submultiple of this number.           2.3. Meters having a cyclic volume less than the value given in the table of item 2.1 of this Chapter may be approved provided that the model satisfies the requirements of the endurance test mentioned in this connection in item 7.2.5 of this Chapter.                  3. Details of construction      3.1. For each of the meters the difference between the calculated value of the cyclic volume V and the value of this volume specified on the meter must not exceed 5 % of the latter.           3.2. Meters G 1 76 to G 6 inclusive may be provided with a device to prevent operation of the counter when the gas flows in a non-authorised direction.                  4. Test element      4.1. For meters G 1 76 to G 6 inclusive the test element is manufactured as indicated in item 5.2.2 of Chapter I. For meters G 10 to G 650 inclusive the test element is:        - either manufactured as in item 5.2.2 of Chapter I;               - or is detachable.                          4.2. When the test element is manufactured as in item 5.2.2 of Chapter I B the value of the scale division of the element and its graduation must satisfy the requirements of the type as shown in the following table : >PIC FILE= "T0038185">             4.3. For meters of which the test element is manufactured as in item 5.2.2 of Chapter I B, the typical deviation for a series of at least thirty successive measurements, carried out at a flow of the order of 0 71 Qmax, and under the same conditions, of a volume of air specified below must exceed the values in the following table: >PIC FILE= "T0038186">                   5. Maximum permissible errors      5.1. General Provisions        5.1.1. The maximum permissible errors, positive or negative, are given in the following table: >PIC FILE= "T0038187">                5.1.2. In EEC initial verification the errors for a meter for flows Q between 2 Qmin and Qmax must not all exceed 1 % if they are all of the same sign.                                 6. Pressure absorption      6.1. Total pressure absorption  The total pressure absorption with a flow of air of density 1 72 kg/m3 at a flow rate equal to Qmax must not exceed on average: >PIC FILE= "T0038188">            6.2. Mechanical pressure absorption  The mechanical pressure absorption, that is to say the absorption of pressure with a flow of air of density 1 72 kg/m3 at a flow between Qmin and 2 Qmin must not exceed: >PIC FILE= "T0038189">   The above values relate to the maximum of the mechanical pressure absorption.            6.3. Special provision  For meters for which the operating pressure exceeds 0 71 MN/m2 (1 bar) the provisions of item 6.2 of this Chapter regarding the mechanical pressure absorption apply, but the total pressure absorption mentioned in item 6.1 of this Chapter of these meters is not taken into consideration.                  7. EEC type approval      7.1. As well as the type sample the applicant must place initially at the disposal of the competent authority two to six further sample meters manufactured in accordance with the type sample.  The number is to be spread over several G sizes at the request of the competent authority if the application for approval covers meters of different sizes.  If the results of the tests are not wholly satisfactory further sample meters may be called for.        7.1.1. A derogation from this provision may be allowed in that these sample meters be placed at the disposal of the competent authority at a later date. However, the decision regarding type approval will not be taken until all samples have been fully examined.               7.1.2. The sample meters shall remain the property of the applicant and will be returned to him after type approval has been granted.                          7.2. The examination        7.2.1. The type sample and the sample meters must satisfy the requirements of Chapter I and items 2, 3, 4, 5 and 6 of this Chapter.               7.2.2. In addition, over the range, the difference between the maximum and the minimum of errors as a function of the flow rate Q must not exceed 3 % for each meter.               7.2.3. The type sample and the sample meters shall be subjected to an endurance test. This test is carried out:          7.2.3.1. For meters G 1 76 to G 10 inclusive : at the maximum meter capacities and with air : however, for meters on which the badge plate specifies the gas to be metered, the test may be effected wholly or partly with this gas.                   7.2.3.2. For meters G 16 to G 650 inclusive : so far as possible at the maximum capacity of the meter with air or with gas.                                  7.2.4. The duration of the endurance test for meters of which the cyclic volume is equal to or greater than the values mentioned in the Table of item 2.1 of this Chapter shall be:          7.2.4.1. For meters G 1 76 to G 10 inclusive : 1000 hrs. The test may be interrupted but must be completed within sixty days.                   7.2.4.2. For meters G 16 to G 650 inclusive : such that each meter will measure a volume of air or of gas corresponding to an operation of 1000 hrs at the maximum output of the meter ; the test must be completed within the six-month period.                                  7.2.5. For meters of which the cyclic volume is less than the values specified in the table of item 2.1 of this Chapter, the duration of the endurance test must be of a duration of 2000 hrs and must be carried out on a greater number of meters than that specified in item 7.1 of this Chapter, according to the description of the meter and its general characteristics.               7.2.6. After the endurance test, the meters must satisfy the following requirements:          (a) over the range, the difference between the maximum and minimum errors as a function of the flow Q must not exceed, for each meter, a value of 4 %;                   (b) at no point should the errors be more than 1 75 % greater than the maximum or less than the minimum initial error;                   (c) the mechanical pressure absorption must not have increased by more than 20 N/m2 (0 72 mbar);                   (d) for meters for which the operating pressure ist greater than 0 71 MN/m2 (1 bar), the difference between the error at flow rate 0 75 Qmax and the error at flow rate Qmax must not have increased by more than 1 %.                                              7.3. Modification of a model already approved  If the request for approval concerns a modification to a model already approved, the metrology service which approved the primary model shall decide, according to the nature of the modification, whether and to what extent the provisions of items 7.1, 7.2.3, 7.2.4 and 7.2.5 of this Chapter are applicable.                  8. EEC initial verification      8.1. Accuracy tests  A meter is considered to satisfy the requirements concerning maximum permissible errors if these requirements are met at the following flow rates:        (a) at a flow rate between Qmin and 2 Qmin;               (b) at a flow rate of the order of 1/5 Qmax;               (c) at a flow rate of Qmax;               (d) at a flow rate 0 750 Qmax for meters which the operating pressure is greater than 0 71 MN/m2 (1 bar).  If the examination is conducted under different conditions, the guarantees must be at least equal to those obtained by the tests mentioned above.                  CHAPTER III PROVISIONS CONCERNING GAS METERS WITH ROTARY PISTONS OR TURBINES     1. Field of application  The present Chapter applies, together with the provisions of Chapter I, to:      1.1. Rotary piston gas meters  - in which the measurement of gas passed is effected by means of measuring chambers with rotary walls.           1.2. Turbine gas meters  - in which the axial flow of gas rotates a turbine wheel and the number of revolutions of the wheel represents the volume of gas passed.                  2. Range of capacities      2.1. Gas meters shall have only the ranges shown in the following table which correspond to their designation(G): >PIC FILE= "T0038190">   and decimal multiples of the last five lines.                   3. Details of construction      3.1. Rotary Piston Meters        3.1.1. Meters should include upstream and downstream static pressure tappings of 3 to 5 millimetre diameter to permit measurement of the pressure drop : the pressure measured upstream will constitute the reference pressure.               3.1.2. The meters may incorporate a manual arrangement for turning the pistons provided that it cannot be used in such a way as to interfere with the correct operation of the meter.               3.1.3. The bearings of the shafts of the rotary pistons of meters of sizes G160 and above may be constructed in such a way as to provide access to them without breaking the protective seals.                          3.2. Turbine Meters        3.2.1. The meters must incorporate a pressure tapping permitting, if necessary indirectly, the determination of the pressure immediately upstream of the turbine wheel as a reference pressure.          3.2.1.1. If there is a device for throttling the gas flow upstream of the rotor, the meter may incorporate, as well as the pressure tapping required by item 3.2.1 of this Chapter, another pressure tapping immediately before the throttle to permit determination of the pressure drop across the throttling device.                                             3.3. Pressure Tappings        3.3.1. These pressure tappings must be provided with means for closing them.               3.3.2. The pressure tappings for the reference pressure must be clearly and indelibly marked "pr" and the pressure tapping should be indicated as "p".                                 4. Test element      4.1. In applying the provisions of item 5.1.1.2 (a) and (b) of Chapter I B, the maximum value of the scale unit of the test element must be: >PIC FILE= "T0038191">            4.2. The scale of the test element must be numbered: >PIC FILE= "T0038192">                   5. Maximum permissible errors      5.1. The maximum permissible errors, positive and negative, are given in the following table: >PIC FILE= "T0038193">            5.2. The errors must not all exceed half the maximum permissible error if they are all of the same sign.                   6. EEC type approval      6.1. As well as the type sample, the applicant must place initially at the disposal of the competent authority two to six sample meters manufactured in accordance with the type sample.  At the request of the competent authority this number shall be spread over several G sizes in the case of a request for approval covering meters of different sizes.  If the results of the tests are not wholly satisfactory supplementary samples may be called for.        6.1.1. A derogation from this provision may be allowed in that these sample meters may be placed at the disposal of the competent authority at a later date. However, the decision regarding type approval will not be taken until all samples have been fully examined.               6.1.2. The sample meters shall remain the property of the applicant and be returned to him after type approval has been granted.                          6.2. Examination        6.2.1. The examination will include in particular the determination of the errors of each meter, by a test with air of density 1 72 kg/m3. Each test result shall be taken into separate consideration.          6.2.1.1. The error curve of each of the meters must remain within the band given by the limits of the maximum permissible errors of EEC initial verifications over the range of flow rates for which approval is requested.                   6.2.1.2. The difference between the maximum value and minimum value of the errors for each of the meters must not exceed 1 % over the range from 0 75 Qmax to Qmax.                                  6.2.2. The meters shall then be subjected to an endurance test with air or gas.          6.2.2.1. So far as possible the endurance test shall be carried out at the maximum capacity of the meter. The period of operation shall be such that each meter measures a volume of air or gas corresponding to operation for 1000 hrs at its maximum capacity, without this total period of test exceeding six months.                   6.2.2.2. After this endurance test, the meters shall be examined again with air of density 1 72 kg/m3 using the same standard equipment as in the test referred to in item 6.2.1 of this Chapter.  Under these test conditions:            (a) The values of the errors determined at the flows specified in item 7.1 of this Chapter for each meter (with the exception of not more than one) should not differ by more than 1 % from the errors found in the test referred to in item 6.2.1 of this Chapter;                       (b) the difference between the maximum value and the minimum value of the error curve should not exceed, for each of the meters (with the exception of not more than one) 1 75 % over the range 0 75 Qmax to Qmax.                                                                           7. EEC initial verification      7.1. Accuracy tests  A meter is considered to satisfy the requirements concerning the maximum permissible errors if the requirements are met at the following flow rates:        (a) For rotary piston meters:  Qmin, 1 75 Qmin, 0 725 Qmax, 0 75 Qmax and Qmax;               (b) For turbine meters:  Qmin, 1 75 Qmin, 3 Qmin, 0 725 Qmax, 0 75 Qmax and Qmax.  If the examination is conducted under different conditions, the guarantees must be at least equal to those obtained by the tests mentioned above.           7.2. The values specified in item 7.1 of this Chapter may be varied by ±5 %.