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31999L0100

Commission Directive 1999/100/EC of 15 December 1999 adapting to technical progress Council Directive 80/1268/EEC relating to the carbon dioxide emissions and the fuel consumption of motor vehicles (Text with EEA relevance)

Official Journal L 334 , 28/12/1999 P. 0036 - 0040

COMMISSION DIRECTIVE 1999/100/ECof 15 December 1999adapting to technical progress Council Directive 80/1268/EEC relating to the carbon dioxide emissions and the fuel consumption of motor vehicles(Text with EEA relevance)THE COMMISSION OF THE EUROPEAN COMMUNITIES,Having regard to the Treaty establishing the European Community,Having regard to Council Directive 70/156/EEC of 6 February 1970 on the approximation of the laws of the Member States relating to the type-approval of motor vehicles and their trailers(1), as last amended by Directive 98/91/EC of the European Parliament and of the Council(2), and in particular Article 13(2) thereof,Having regard to Council Directive 80/1268/EEC of 16 December 1980 relating to the carbon dioxide emissions and the fuel consumption of motor vehicles(3), as last amended by Commission Directive 93/116/EC(4), and in particular Article 3 thereof,Whereas:(1) Directive 80/1268/EEC is one of the separate Directives of the EC type-approval procedure which was established by Directive 70/156/EEC. Consequently, the provisions laid down in Directive 70/156/EEC relating to vehicle systems, components and separate technical units apply to this Directive.(2) In Directive 98/69/EC of the European Parliament and Council of 13 October 1998 relating to measures to be taken against air pollution from motor vehicles and amending Council Directive 70/220/EEC(5), the type I test cycle for emission measurement was amended by abolishing the initial 40 seconds of engine idle time. It is necessary to align the test cycle for the measurement of CO2 emissions and fuel consumption in Directive 80/1268/EEC accordingly.(3) With a view to the monitoring of CO2 emissions in the framework of the Community strategy to reduce CO2 emissions of passenger cars, it is appropriate to introduce into Directive 80/1268/EEC new technical requirements regarding the measurement of CO2 emissions and fuel consumption for the EC type-approval of gas-fuelled vehicles (LPG and NG). In this respect, it is appropriate to follow the technical requirements adopted by the United Nations Economic Commission for Europe in its Regulation No 101(6).(4) The measures provided for in this Directive are in accordance with the opinion of the Committee for Adaptation to Technical Progress established by Directive 70/156/EEC,HAS ADOPTED THIS DIRECTIVE:Article 1Annexes I and II to Directive 80/1268/EEC are hereby amended in accordance with the Annex to this Directive.Article 21. With effect from 1 January 2000, Member States may not, on grounds relating to the emission of carbon dioxide or to fuel consumption:- refuse, in respect of any given type of motor vehicle, to grant EC type-approval pursuant to Article 4(1) of Directive 70/156/EEC, or- refuse to grant national type-approval, or- prohibit the registration, sale or entry into service of vehicles pursuant to Article 7 of Directive 70/156/EECif the emission and consumption figures have been determined in accordance with the requirements of Directive 80/1268/EEC, as amended by this Directive.2. With effect from 1 January 2000, for vehicles in category M1 as defined in Annex II, Section A, to Directive 70/156/EEC, except vehicles of which the maximum mass exceeds 2500 kg, and with effect from 1 January 2001 for vehicles in category M1 the maximum mass of which exceeds 2500 kg, Member States:- shall no longer grant EC type-approval pursuant to Article 4(1) of Directive 70/156/EEC, and- shall refuse to grant national type-approval, except where the provisions of Article 8(2) of Directive 70/156/EEC are invoked,for a type of vehicle if the emission and consumption figures have not been determined in accordance with the requirements of Directive 80/1268/EEC, as amended by this Directive.3. With effect from 1 January 2001, for vehicles in category M1 as defined in Annex II, Section A, to Directive 70/156/EEC, except vehicles of which the maximum mass exceeds 2500 kg, and with effect from 1 January 2002 for vehicles in category M1 the maximum mass of which exceeds 2500 kg, Member States:- shall consider certificates of conformity which accompany new vehicles in accordance with the provisions of Directive 70/156/EEC to be no longer valid for the purposes of Article 7(1) of that Directive, and- shall refuse the registration, sale and entry into service of new vehicles which are not accompanied by a certificate of conformity in accordance with Directive 70/156/EEC, except where the provisions of Article 8(2) of Directive 70/156/EEC are invoked,if the emission and consumption figures have not been determined in accordance with the requirements of Directive 80/1268/EEC, as amended by this Directive.Article 31. Member States shall bring into force the laws, regulations and administrative provisions necessary to comply with this Directive by 31 December 1999. They shall forthwith inform the Commissin thereof.When Member States adopt those provisions, they shall contain a reference to this Diective or be accompanied by such a reference on the occasion of their official publication. Member States shall determine how such reference is to be made.2. Member States shall communicate to the Commission the texts of the main provisions of national law which they adopt in the field covered by this Directive.Article 4This Directive shall enter into force on the third day following its publication in the Official Journal of the European Communities.Article 5This Directive is addressed to the Member States.Done at Brussels, 15 December 1999.For the CommissionErkki LIIKANENMember of the Commission(1) OJ L 42, 23.2.1970, p. 1.(2) OJ L 11, 16.1.1999, p. 25.(3) OJ L 375, 31.12.1980, p. 36.(4) OJ L 329, 30.12.1993, p. 39.(5) OJ L 350, 28.12.1998, p. 1.(6) UN/ECE Regulation No 101 (E/ECE324-E/ECE/TRANS/505/Rev.2 Add. 100), as amended.ANNEXAMENDMENTS TO ANNEXES I AND II TO DIRECTIVE 80/1268/EECAnnex I is amended as follows:1. Item 4.1 is replaced by the following: "4.1. The CO2 emissions are measured during the test cycle simulating the urban and extra-urban driving patterns as described in Appendix 1 of Annex III to Directive 70/220/EEC, as last amended."2. Item 4.4 is replaced by the following: "4.4. Test fuel4.4.1. Petrol and diesel vehiclesThe appropriate reference fuels as defined in Annex IX to Directive 70/220/EEC, as last amended, must be used for testing.4.4.2. LPG and NG-fuelled vehiclesFor LPG and NG, that fuel must be used which is chosen by the manufacturer for the measurement of the net power in accordance with Annex I to Directive 80/1269/EEC. The chosen fuel shall be specified in the communication document as defined in Annex II.4.4.3. For the purpose of calculation mentioned in 4.3, the following fuel characteristics will be used:(a) density: measured on the test fuel according to ISO 3675 or an equivalent method; for petrol and diesel the measured density at 15 °C will be used; for LPG and NG, a reference density will be used, as follows:0,538 kg/l for LPG0,654 kg/m3 for NG(1)(b) hydrogen-carbon ratio: fixed values will be used, which are:1,85 for petrol1,86 for diesel2,525 for LPG4,00 for NG2,93 for NG (NMHC)"3. Item 5.1.4, second paragraph, is replaced by the following: "At the manufacturer's request, positive ignition engined vehicles may be preconditioned according to the procedure prescribed in item 5.2.1 of Annex VI to Directive 70/220/EEC, as last amended. Compression ignition engined vehicles may be preconditioned according to the procedure described in item 5.3 of Annex III to the same Directive."4. Item 6.1 is replaced by the following: "6.1. Test cycleThe test cycle is described in Appendix 1 of Annex III to Directive 70/220/EEC, as last amended, including both Part I (urban driving) and Part II (extra-urban driving). All driving prescriptions contained in this Appendix will be applied for the CO2 measurement."5. Item 6.3.1 is replaced by the following: "6.3.1. The load and inertia adjustments of the dynamometer are determined as defined in Annex III to Directive 70/220/EEC, as last amended."6. Items 6.3.2 and 6.3.3 are deleted.7. Item 6.4.1.3 is amended to read: "...The dilution factor is calculated as follows:For petrol and diesel:>REFERENCE TO A GRAPHIC>For LPG>REFERENCE TO A GRAPHIC>For NG>REFERENCE TO A GRAPHIC>where: ..."8. Item 7.2 is replaced by the following: "7.2. The fuel consumption, expressed in litres per 100 km (in the case of petrol, LPG or diesel) or in m3 per 100 km (in the case of NG), is calculated by means of the following formulae:(2)(a) for vehicles with a positive ignition engine fuelled with petrol:>REFERENCE TO A GRAPHIC>(b) for vehicles with a positive ignition engine fuelled with LPG:>REFERENCE TO A GRAPHIC>If the composition of the fuel used for the test differs from the composition that is assumed for the calculation of the normalised consumption, on the manufacturer's request a correction factor cf may be applied as follows:>REFERENCE TO A GRAPHIC>The correction factor cf, which may be applied, is determined as follows:>REFERENCE TO A GRAPHIC>where:nactual= the actual H/C ratio of the fuel used(c) for vehicles with a positive ignition engine fuelled with NG:>REFERENCE TO A GRAPHIC>(d) for vehicles with a compression ignition engine:>REFERENCE TO A GRAPHIC>In these formulae:FC= the fuel consumption in litre per 100 km (in the case of petrol, LPG or diesel) or in m3 per 100 km (in the case of NG)THC= the measured emission of total hydrocarbons in g/kmCO= the measured emission of carbon monoxide in g/kmCO2= the measured emission of carbon dioxide in g/kmD= the density of the test fuel at 15 °C."9. Item 9.1.1.2.4 is replaced by the following: "9.1.1.2.4. The reference fuels described in Annex IX and Annex IXa to Directive 70/220/EEC, as last amended, shall be used for testing."Annex II is amended as follows:1. Item 1.7 of the Addendum is replaced by the following: ">PIC FILE= "L_1999334EN.004001.EPS">"2. The following footnotes are added at the end of the Addendum: "(4) Repeat for petrol and gaseous fuel in the case of a vehicle that can run either on petrol or on a gaseous fuel. Vehicles that can be fuelled with both petrol and a gaseous fuel, but where the petrol system is fitted for emergency purposes or starting only and of which the petrol tank cannot contain more than 15 litres of petrol will be regarded for the test as vehicles which can only run a gaseous fuel.(5) For vehicles fuelled with NG, the unit "l/100 km" is replaced by "m3/100 km"."(1) This is the mean value of the G20 and G23 reference fuels at 15 °C.(2) Repeat for petrol and gaseous fuel in the case of a vehicle that can run either on petrol or on a gaseous fuel. Vehicles that can be fuelled with both petrol and a gaseous fuel, but where the petrol system is fitted for emergency purposes or starting only and of which the petrol tank cannot contain more than 15 litres of petrol will be regarded for the test as vehicles which can only run a gaseous fuel.


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31992L0112

Council Directive 92/112/EEC of 15 December 1992 on procedures for harmonizing the programmes for the reduction and eventual elimination of pollution caused by waste from the titanium dioxide industry

Official Journal L 409 , 31/12/1992 P. 0011 - 0016 Finnish special edition: Chapter 15 Volume 12 P. 0032  Swedish special edition: Chapter 15 Volume 12 P. 0032

COUNCIL DIRECTIVE 92/112/EEC of 15 December 1992 on procedures for  harmonizing the programmes for the reduction and eventual elimination of pollution caused by waste  from the titanium dioxide industryTHE COUNCIL OF THE EUROPEAN COMMUNITIES, Having regard to the Treaty establishing the European Economic Community, and in particular Article  100a thereof, Having regard to the proposal from the Commission  (1), In cooperation with the European Parliament  (2), Having regard to the opinion of the Economic and Social Committee  (3), Whereas Council Directive 89/428/EEC of 21 June 1989 on procedures for harmonizing the programmes  for the reduction and eventual elimination of pollution caused by waste from the titanium dioxide  industry  (4) was annulled by the Court of Justice in its judgment of 11 June 1991 on the grounds  that it lacked an appropriate legal basis  (5); Whereas, if Member States have taken the necessary measures to comply with the said Directive, it  is not necessary for them to adopt new measures to meet this Directive, provided the measures  already taken comply with the latter; Whereas the legal void caused by the annulment of the said Directive may have adverse effects on  the environment and on conditions of competition in the titanium dioxide production sector; whereas  it is necessary to restore the material situation created by the said Directive; Whereas the objective of this Directive is to approximate national rules relating to titanium  dioxide production conditions in order to eliminate the existing distortions of competition between  the various producers in the industry and to ensure a high level of environmental protection; Whereas Council Directive 78/176/EEC of 20 February 1978 on waste from the titanium dioxide  industry  (6), and in particular Article 9 thereof, requires the Member States to draw up  programmes for the progressive reduction and eventual elimination of pollution caused by waste from  industrial establishments in existence on 20 February 1978; Whereas these programmes set general targets for the reduction of pollution caused by liquid, solid  and gaseous wastes to be achieved by 1 July 1987; whereas these programmes were to be submitted to  the Commission so that it could present suitable proposals to the Council for their harmonization  with regard to the reduction and eventual elimination of this pollution and the improvement of the  conditions of competition in the titanium dioxide industry; Whereas, in order to protect the aquatic environment, dumping of waste and discharges of certain  wastes, in particular of solid and strong acid wastes, should be prohibited and discharges of other  wastes, in particular of weak acid and neutralized wastes, should be progressively reduced; Whereas existing industrial establishments should employ the appropriate systems for treating the  wastes in order to meet the requisite targets by the set dates; Whereas installation of those systems can give rise to major technico-economic difficulties in the  case of weak acid waste and neutralized waste from certain establishments; whereas Member States  should therefore be able to defer application of these provisions, on condition that a programme of  effective reduction of pollution is drawn up and submitted to the Commission; whereas where Member  States experience such difficulties, the Commission should be able to extend the relevant time  limits; Whereas, in respect of discharges of certain wastes, Member States should be able to make use of  quality objectives in such a way that the results are equivalent in all respects to those obtained  through limit values; whereas such equivalence should be demonstrated in a programme to be  presented to the Commission; Whereas, without prejudice to the obligations placed on Member States by Council Directive  80/779/EEC of 15 July 1980 on air quality limit values and guide values for sulphur dioxide and  suspended particulates  (1), and Council Directive 84/360/EEC of 28 June 1984 on the combating of  air pollution from industrial plants  (2), it is expedient to protect the quality of the air by  fixing appropriate emission standards in respect of gaseous discharges from the titanium dioxide  industry; Whereas, in order to verify the effective application of the measures, Member States should  undertake monitoring in relation to the actual production of each establishment; Whereas all waste from the titanium dioxide industry should be avoided or reused where technically  and economically feasible and whereas such waste should be reused or disposed of without  endangering human health or the environment, HAS ADOPTED THIS DIRECTIVE:Article 1This Directive lays down, as required by  Article 9  (3) of Directive 78/176/EEC, procedures for harmonizing the programmes for the reduction  and eventual elimination of pollution from existing industrial establishments and is intended to  improve the conditions of competition in the titanium dioxide industry. Article 21.    For the purposes of this Directive: (a)   where the sulphate process is used: -   solid waste shall mean: -   insoluble ore residues not broken down by sulphuric acid during the manufacturing proces,  - copperas, i.  e. crystalline ferrous sulphate (FeSO47H2O),  - strong acid waste shall mean: - the mother liquors arising from the filtration phase following hydrolysis of the titanyl sulphate  solution. If these mother liquors are associated with weak acid wastes which overall contain more  than 0,5  % free sulphuric acid and various heavy metals  (3), the liquors and waste taken together  shall be considered strong acid waste,  - treatment waste shall mean: - filtration salts, sludges and liquid waste arising from the treatment (concentration or  neutralization) of strong acid waste and containing various heavy metals, but not including  neutralized and filtered or decanted waste containing only traces of heavy metals and which, before  any dilution, has a pH value above 5,5,  - weak acid waste shall mean: - wash waters, cooling waters, condensates and other sludges and liquid wastes, other than those  included in the above definitions, containing 0,5  % or less free sulphuric acid,  - neutralized waste shall mean: - any liquid which has a pH value over 5,5, contains only traces of heavy metals, and is obtained  directly by filtration or decantation from strong or weak acid waste after its treatment to reduce  its acidity and its heavy metal content,  - dust shall mean: - all kinds of dust from production plants and in particular ore and pigment dust,  - SOx shall mean: - gaseous sulphur dioxide and trioxide released in the various stages of the manufacturing and  internal waste treatment processes, including acid droplets; (b) where the chlorine process is used: - solid waste shall mean: - insoluble ore residues not broken down by the chlorine during the manufacturing process,  - metal chlorides and metal hydroxides (filtration substances), arising in solid form from the  manufacture of titanium tetrachloride,  - coke residues arising from the manufacture of titanium tetrachloride,  - strong acid waste shall mean: - waste containing more than 0,5  % free hydrochloric acid and various heavy metals  (1);  - treatment waste shall mean: - filtration salts, sludges and liquid waste arising from the treatment (concentration or  neutralization) of strong acid waste and containing various heavy metals, but not including  neutralized and filtered or decanted waste containing only traces of heavy metals and which, before  any dilution, has a pH value over 5,5,  - weak acid waste shall mean: - wash waters, cooling waters, condensates and other sludges and liquid wastes, other than those  included in the above definitions, containing 0,5  % or less free hydrochloric acid,  - neutralized waste shall mean: - any liquid which has a pH value over 5,5, contains only traces of heavy metals, and is obtained  directly by filtration or decantation from strong or weak acid waste after its treatment to reduce  its acidity and its heavy metal content,  - dust shall mean: - all kinds of dust from production plants and in particular ore, pigment and coke dust,  - chlorine shall mean: - gaseous chlorine released in the various stages of the manufacturing process; (c) where the sulphate process or the chlorine process is used- dumping shall mean: - any deliberate disposal into inland surface waters, internal coastal waters, territorial waters  or the high seas of substances and materials by or from ships or aircraft  (2)2.    The terms  defined in Directive 78/176/EEC shall have the same meaning for the purposes of this  Directive.Article 3The dumping of any solid waste, strong acid waste, treatment waste, weak acid  waste, or neutralized waste, as referred to in Article 2 shall be prohibited with effect from 15  June 1993.Article 4Member States shall take the necessary measures to ensure that discharges of  waste into inland surface waters, internal coastal waters, territorial waters and the high sea are  prohibited: (a)   as regards solid waste, strong acid waste and treatment waste from existing industrial  establishments using the sulphate process: -   by 15 June 1993 in all the abovementioned waters; (b) as regards solid waste and strong acid waste from existing industrial establishments using the  chlorine process: - by 15 June 1993 in all the abovementioned waters.Article 5In the case of Member States which  have serious technical and economic difficulties in complying with the date of application referred  to in Article 4, the Commission may grant an extension, provided that a programme for the effective  reduction of discharges of such waste is submitted to the Commission by 15 June 1993. That  programme must result in a definitive ban on such discharges by 30 June 1993. No later than three months after adoption of this Directive, the Commission shall be informed of  any such cases and shall be consulted thereon. The Commission shall inform the other Member  States.Article 6Member States shall take the necessary measures to ensure that discharges of  waste are reduced in accordance with the following provisions: (a)   from existing industrial establishments using the sulphate process: -   weak acid waste and neutralized waste shall be reduced by 31 December 1993 in all waters to a  value of not more than 800 kg of total sulphate per tonne of titanium dioxide produced (i.  e.  corresponding to the SO4 ions contained in the free sulphuric acid and in the metallic sulphates); (b) from existing industrial establishments using the chlorine process: - weak acid waste, treatment waste and neutralized waste shall be reduced by 15 June 1993 in all  waters to the following values of total chloride per tonne of titanium dioxide produced (i.  e.  corresponding to the C1 ions contained in the free hydrochloric acid and in the metallic  chlorides): -   130 kg using neutral rutile,  - 228 kg using synthetic rutile,  - 450 kg using slag. In the case of an establishment using more than one type or ore, the values shall apply in  proportion to the quantity of these ores used.Article 7Except where inland surface waters are  concerned, Member States may defer the date of application referred to in point (a) of Article 6  until 31 December 1994 at the latest if serious technico-economic difficulties so require and  provided that a programme of effective reduction of discharges of such waste is submitted to the  Commission by 15 June 1993. Such a programme shall enable the following limit value per tonne of  titanium dioxide produced to be reached by the date shown: -   weak acid waste and neutralized waste: 1  200 kg - 15 June 1993, - weak acid waste and neutralized waste: 800 kg - 31 December 1994. Three months at the latest following adoption of this Directive the Commission shall be informed of  such cases, which shall be the subject of consultation with the Commission. The Commission shall  inform the other Member States.Article 81.    As regards the requirements of Article 6, Member  States may choose to make use of quality objectives coupled with appropriate limit values applied  in such a way that the effects in terms of protecting the environment and avoiding distortions of  competition are equivalent to that of the limit values laid down in this Directive. 2.    If a Member State chooses to make use of quality objectives, it shall present to the  Commission a programme  (1) demonstrating that the measures achieve an effect which, in terms of  protecting the environment and avoiding distortion of competition, is equivalent to that of the  limit values by the dates when these limit values are applied in accordance with Article 6. This programme shall be submitted to the Commission at least six months before the Member State  proposes to apply the quality objectives. This programme shall be assessed by the Commission in accordance with the procedures laid down in  Article 10 of Directive 78/176/EEC. The Commission shall inform the other Member States.Article 91.    Member States shall take the  necessary measures to ensure that discharges into the atmosphere are reduced in accordance with the  following provisions: (a)   in the case of existing industrial establishments using the sulphate process: (i)   as regards dust, discharges shall be reduced by 31 December 1993 to a value of not more than  50 mg/nm3  (2) from major sources and not more than 150 mg/nm3  (2) from any other source  (3);  (ii) as regards S0x, discharges arising from digestion and calcination steps in the manufacture of  titanium dioxide shall be reduced by 1 January 1995 to a value of not more than 10 kg of SO2   equivalent per tonne of titanium dioxide produced;  (iii) Member States shall require means to be installed for preventing the emission of acid  droplets;  (iv) plants for the concentration of waste acid shall not discharge more than 500 mg/nm3 SOx   calculated as SO2 equivalent  (1);  (v) plants for the roasting of salts generated by the treatment of waste shall be equipped with  the best available technology not entailing excessive costs in order to reduce SOx emissions; (b)   in the case of existing industrial establishments using the chlorine process: (i)   as regards dust, discharges shall be reduced by 15 June 1993 to a value of not more than 50  mg/nm3  (2) for major sources and not more than 150 mg/nm3  (2) from any other source  (3);  (ii) as regards chlorine, discharges shall be reduced by 15 June 1993 to a daily average  concentration of not more than 5 mg/nm3  (4) and not more than 40 mg/ng3 at any time. 2.    This Directive shall not prejudice Directive 80/779/EEC. 3.    The procedure for monitoring the reference measurements for discharges of SOx into the  atmosphere is set out in the Annex.Article 10Member States shall monitor the values and  reductions specified in Articles 6, 8 and 9 in relation to the actual production of each  establishment.Article 11Member States shall take the measures necessary to ensure that all waste  from the titanium dioxide industry, and in particular waste subject to prohibition on discharge or  dumping into water or on discharge into the atmosphere is: -   avoided or reused where technically and economically feasible, - reused or disposed of without endangering human health or harming the environment. The same shall apply to waste arising from the reuse or treatment of the abovementioned  waste.Article 121.    Member States which have not yet taken the necessary measures to comply  with this Directive shall bring them into force not later than 15 June 1993. They shall inform the  Commission forthwith of the national provisions adopted to comply with this Directive. When Member States adopt these provisions, they shall contain a reference to this Directive or  shall be accompanied by such reference at the time of their official publication. The procedure for  such reference shall be adopted by Member States. 2.    Member States shall communicate to the Commission the provisions of national law which they  adopt in the field governed by this Directive. Article 13This Directive is addressed to the Member States. Done at Brussels, 15 December 1992. For the CouncilThe PresidentM. HOWARD (1)  OJ No C 317, 7. 12. 1991, p. 5.  (2)  OJ No C 94, 13. 4. 1992, p. 158, andOJ No C 305, 23. 11. 1992.  (3)  OJ No C 98, 21. 4. 1992, p. 9.  (4)  OJ No L 201, 14. 7. 1989, p. 56.  (5)Judgment of 11 June 1991, Case C-300/89, Commission v. Council (not yet published).  (6)  OJ No L 54, 25. 2. 1978, p. 19; Directive as last amended by Directive 83/29(EEC (OJ No L 32,  3. 2. 1983, p. 28).  (1)  OJ No L 229, 30. 8. 1980, p. 30; Directive as last amended by Directive 89/427/EEC (OJ No L  201, 14. 7. 1989, p. 53).  (2)  OJ No L 188, 16. 7. 1989, p. 20.  (3)  Strong acid waste which has been diluted until it contains 0,5  % or less free sulphuric acid  shall also be covered by this difinition.  (1)Strong acid waste which has been diluted until it contains 0,5  % or less free sulphuric acid  shall also be covered by this definition.  (2)  'Ships and aircraft` shall mean waterborne vessels and airborne craft of any type whatsoever.  This expression shall include air-cushion craft, floating craft, whether self-propelled or not, and  fixed or floating platforms.  (1)  Such information shall be provided under Article 14 of Directive 78/176/EEC or separately  should circumstances so require.  (2)Cubic metre at a temperature of 273  K and a pressure of 101,3 kPa.  (3)Member States shall inform the Commission of those minor sources not included in their  measurements.  (1)  For new concentration processes the Commission can agree to a different value if the Member  States can demonstrate the non-availability of techniques to achieve this standard.  (2)Cubic meter at a temperature of 273  K and a pressure of 101,3 kPa.  (3)Member States shall inform the Commission of those minor sources not included in their  measurements.  (4)It is considered that these values correspond to a maximum of six grammes per tonne of titanium  dioxide produced.   ANNEX Procedure for monitoring the reference measurements for gaseous SOx emissions For  the purposes of calculating the quantities of SO2 and SO3 and acid droplets expressed as SO2  equivalent, discharged by specific installations, account must be taken of the volume of gas  discharged over the duration of the specific operations in question and of the average SO2/SO3  content measured over the same period. The SO2/SO3 flow rate and content must be determined under  the same temperature and humidity conditions.


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32002L0003

Directive 2002/3/EC of the European Parliament and of the Council of 12 February 2002 relating to ozone in ambient air

Official Journal L 067 , 09/03/2002 P. 0014 - 0030

Directive 2002/3/EC of the European Parliament and of the Councilof 12 February 2002relating to ozone in ambient airTHE EUROPEAN PARLIAMENT AND THE COUNCIL OF THE EUROPEAN UNION,Having regard to the Treaty establishing the European Community, and in particular Article 175(1) thereof,Having regard to the proposal from the Commission(1),Having regard to the opinion of the Economic and Social Committee(2),Having regard to the opinion of the Committee of the Regions(3),Acting in accordance with the procedure laid down in Article 251 of the Treaty(4), in light of the joint text approved by the Conciliation Committee on 10 December 2001,Whereas:(1) On the basis of principles enshrined in Article 174 of the Treaty, the Fifth Environmental Action Programme, approved by the Resolution of the Council and the Representatives of the Governments of the Member States meeting within the Council of 1 February 1993 on a European Community programme of policy and action in relation to the environment and sustainable development(5) and supplemented by Decision No 2179/98/EC(6) envisages, in particular, amendments to existing legislation on air pollutants. The said programme recommends the establishment of long-term air quality objectives.(2) Pursuant to Article 4(5) of Council Directive 96/62/EC of 27 September 1996 on ambient air quality assessment and management(7), the Council is to adopt the legislation provided for in paragraph 1 and the provisions laid down in paragraphs 3 and 4 of that Article.(3) It is important to ensure effective protection against harmful effects on human health from exposure to ozone. The adverse effects of ozone on vegetation, ecosystems and the environment as a whole should be reduced, as far as possible. The transboundary nature of ozone pollution requires measures to be taken at Community level.(4) Directive 96/62/EC provides that numerical thresholds are to be based on the findings of work carried out by international scientific groups active in the field. The Commission is to take account of the most recent scientific research data in the epidemiological and environmental fields concerned and of the most recent advances in metrology with a view to re-examining the elements on which such thresholds are based.(5) Directive 96/62/EC requires limit and/or target values to be set for ozone. In view of the transboundary nature of ozone pollution, target values should be set at Community level for the protection of human health and for the protection of vegetation. Those target values should relate to the interim objectives derived from the Community integrated strategy to combat acidification and ground-level ozone, which also form the basis of Directive 2001/81/EC of the European Parliament and of the Council of 23 October 2001 on national emission ceilings for certain atmospheric pollutants(8).(6) In accordance with Directive 96/62/EC, plans and programmes should be implemented in respect of zones and agglomerations within which ozone concentrations exceed target values in order to ensure that target values are met as far as possible by the date specified. Such plans and programmes should to a large extent refer to control measures to be implemented in accordance with relevant Community legislation.(7) Long-term objectives should be set with the aim of providing effective protection of human health and the environment. Long-term objectives should relate to the ozone and acidification abatement strategy and its aim of closing the gap between current ozone levels and the long-term objectives.(8) Measurements should be mandatory in zones with exceedances of the long-term objectives. Supplementary means of assessment may reduce the required number of fixed sampling points.(9) An alert threshold for ozone should be set for the protection of the general population. An information threshold should be set to protect sensitive sections of the population. Up-to-date information on concentrations of ozone in ambient air should be routinely made available to the public.(10) Short-term action plans should be drawn up where the risk of exceedances of the alert threshold can be reduced significantly. The potential for reducing the risk, duration and severity of exceedances should be investigated and assessed. Local measures should not be required where examination of benefits and costs shows them to be disproportionate.(11) The transboundary nature of ozone pollution may require some coordination between neighbouring Member States in drawing up and implementing plans, programmes and short-term action plans and in informing the public. Where appropriate, Member States should pursue cooperation with third countries, with particular emphasis on early involvement of accession candidate countries.(12) As a basis for regular reports, information on measured concentrations should be submitted to the Commission.(13) The Commission should review the provisions of this Directive in the light of the most recent scientific research concerning, in particular, the effects of ozone on human health and the environment. The Commission's report should be presented as an integral part of an air quality strategy designed to review and propose Community air quality objectives and develop implementing strategies to ensure achievement of those objectives. In this context, the report should take into account the potential to achieve the long-term objectives within a specified time period.(14) The measures necessary for the implementation of this Directive should be adopted in accordance with Council Decision 1999/468/EC of 28 June 1999 laying down the procedures for the exercise of implementing powers conferred on the Commission(9).(15) Since the objectives of the proposed action ensuring effective protection against harmful effects on human health from ozone and reducing the adverse effect of ozone on vegetation, ecosystems and the environment as a whole cannot be sufficiently achieved by the Member States because of the transboundary nature of ozone pollution and can therefore be better achieved at Community level, the Community may adopt measures, in accordance with the principle of subsidiarity as set out in Article 5 of the Treaty. In accordance with the principle of proportionality, as set out in that Article, this Directive does not go beyond what is necessary in order to achieve those objectives.(16) Council Directive 92/72/EEC of 21 September 1992 on air pollution by ozone(10) should be repealed,HAVE ADOPTED THIS DIRECTIVE:Article 1ObjectivesThe purpose of this Directive is:(a) to establish long-term objectives, target values, an alert threshold and an information threshold for concentrations of ozone in ambient air in the Community, designed to avoid, prevent or reduce harmful effects on human health and the environment as a whole;(b) to ensure that common methods and criteria are used to assess concentrations of ozone and, as appropriate, ozone precursors (oxides of nitrogen and volatile organic compounds) in ambient air in the Member States;(c) to ensure that adequate information is obtained on ambient levels of ozone and that it is made available to the public;(d) to ensure that, with respect to ozone, ambient air quality is maintained where it is good, and improved in other cases;(e) to promote increased cooperation between the Member States, in reducing ozone levels, use of the potential of transboundary measures and agreement on such measures.Article 2DefinitionsFor the purposes of this Directive:1. "ambient air" means outdoor air in the troposphere, excluding work places;2. "pollutant" means any substance introduced directly or indirectly by man into the ambient air and likely to have harmful effects on human health and/or the environment as a whole;3. "ozone precursor substances", means substances which contribute to the formation of ground-level ozone, some of which are listed in Annex VI;4. "level" means the concentration of a pollutant in ambient air or the deposition thereof on surfaces in a given time;5. "assessment" means any method used to measure, calculate, predict or estimate the level of a pollutant in the ambient air;6. "fixed measurements" means measurements taken in accordance with Article 6(5) of Directive 96/62/EC;7. "zone" means part of the territory of a Member State as delimited by it;8. "agglomeration" means a zone with a population concentration in excess of 250000 inhabitants or, where the population concentration is 250000 inhabitants or less, a population density per km² which for the Member State justifies the need for ambient air quality to be assessed and managed;9. "target value" means a level fixed with the aim, in the long term, of avoiding harmful effects on human health and/or the environment as a whole, to be attained where possible over a given period;10. "long-term objective" means an ozone concentration in the ambient air below which, according to current scientific knowledge, direct adverse effects on human health and/or the environment as a whole are unlikely. This objective is to be attained in the long term, save where not achievable through proportionate measures, with the aim of providing effective protection of human health and the environment;11. "alert threshold" means a level beyond which there is a risk to human health from brief exposure for the general population and at which immediate steps shall be taken by the Member States as laid down in Articles 6 and 7;12. "information threshold" means a level beyond which there is a risk to human health from brief exposure for particularly sensitive sections of the population and at which up-to-date information is necessary;13. "volatile organic compounds" (VOC) means all organic compounds from anthropogenic and biogenic sources, other than methane, that are capable of producing photochemical oxidants by reactions with nitrogen oxides in the presence of sunlight.Article 3Target values1. The target values for 2010 in respect of ozone concentrations in ambient air are those set out in Section II of Annex I.2. Member States shall draw up a list of zones and agglomerations in which the levels of ozone in ambient air, as assessed in accordance with Article 9, are higher than the target values referred to in paragraph 1.3. For the zones and agglomerations referred to in paragraph 2, Member States shall take measures to ensure, in accordance with the provisions of Directive 2001/81/EC, that a plan or programme is prepared and implemented in order to attain the target value, save where not achievable through proportionate measures, as from the date specified in Section II of Annex I.Where, in accordance with Article 8(3) of Directive 96/62/EC, plans or programmes must be prepared or implemented in respect of pollutants other than ozone, Member States shall, where appropriate, prepare and implement integrated plans or programmes covering all the pollutants concerned.4. The plans or programmes, referred to in paragraph 3, shall incorporate at least the information listed in Annex IV to Directive 96/62/EC and shall be made available to the public and to appropriate organisations such as environmental organisations, consumer organisations, organisations representing the interests of sensitive population groups and other relevant health care bodies.Article 4Long-term objectives1. The long-term objectives for ozone concentrations in ambient air are those set out in Section III of Annex I.2. Member States shall draw up a list of the zones and agglomerations in which the levels of ozone in ambient air, as assessed in accordance with Article 9, are higher than the long-term objectives referred to in paragraph 1 but below, or equal to, the target values set out in Section II of Annex I. For such zones and agglomerations, Member States shall prepare and implement cost-effective measures with the aim of achieving the long-term objectives. The measures taken shall, at least, be consistent with all plans or programmes specified in Article 3(3). Furthermore, they shall build upon measures taken under the provisions of Directive 2001/81/EC and other relevant existing and future EC legislation.3. Community progress towards attaining the long-term objectives shall be subject to successive reviews, as part of the process set out in Article 11 and in connection with Directive 2001/81/EC, using the year 2020 as a benchmark and taking account of progress towards attaining the national emission ceilings set out in the said Directive.Article 5Requirements in zones and agglomerations where ozone levels meet the long-term objectivesMember States shall draw up a list of zones and agglomerations in which ozone levels meet the long-term objectives. In so far as factors including the transboundary nature of ozone pollution and meteorological conditions permit, they shall maintain the levels of ozone in those zones and agglomerations below the long-term objectives and shall preserve through proportionate measures the best ambient air quality compatible with sustainable development and a high level of environmental and human health protection.Article 6Information to the public1. Member States shall take appropriate steps to:(a) ensure that up-to-date information on concentrations of ozone in ambient air is routinely made available to the public as well as to appropriate organisations such as environmental organisations, consumer organisations, organisations representing the interests of sensitive population groups and other relevant health care bodies.This information shall be updated on at least a daily basis and, wherever appropriate and practicable, on an hourly basis.Such information shall at least indicate all exceedances of the concentrations in the long-term objective for the protection of health, the information threshold and the alert threshold for the relevant averaging period. It should also provide a short assessment in relation to effects on health.The information threshold and the alert threshold for concentrations of ozone in ambient air are given in Section I of Annex II;(b) make available to the public and to appropriate organisations such as environmental organisations, consumer organisations, organisations representing the interests of sensitive population groups and other relevant health care bodies comprehensive annual reports which shall at least indicate, in the case of human health, all exceedances of concentrations in the target value and the long-term objective, the information threshold and the alert threshold, for the relevant averaging period, and in the case of vegetation, any exceedance of the target value and the long-term objective, combined with, as appropriate, a short assessment of the effects of these exceedances. They may include, where appropriate, further information and assessments on forest protection, as specified in section I of Annex III. They may also include information on relevant precursor substances, in so far as these are not covered by existing Community legislation;(c) ensure that timely information about actual or predicted exceedances of the alert threshold is provided to health care institutions and the population.The information and reports referred to above shall be published by appropriate means, depending on the case, for example the broadcasting media, the press or publications, information screens or computer network services, such as the internet.2. Details supplied to the public in accordance with Article 10 of Directive 96/62/EC when either threshold is exceeded shall include the items listed in Section II of Annex II. Member States shall, where practicable, also take steps to supply such information when an exceedance of the information threshold or alert threshold is predicted.3. Information supplied under paragraphs 1 and 2 shall be clear, comprehensible and accessible.Article 7Short-term action plans1. In accordance with Article 7(3) of Directive 96/62/EC, Member States shall draw up action plans, at appropriate administrative levels, indicating specific measures to be taken in the short term, taking into account particular local circumstances, for the zones where there is a risk of exceedances of the alert threshold, if there is a significant potential for reducing that risk or for reducing the duration or severity of any exceedance of the alert threshold. Where it is found that there is no significant potential for reducing the risk, duration or severity of any exceedance in the relevant zones, Member States shall be exempt from the provisions of Article 7(3) of Directive 96/62/EC. It is for Member States to identify whether there is significant potential for reducing the risk, duration or severity of any exceedance, taking account of the national geographical, meteorological and economic conditions.2. The design of short-term action plans, including trigger levels for specific actions, is the responsibility of Member States. Depending on the individual case, the plans may provide for graduated, cost-effective measures to control and, where necessary, reduce or suspend certain activities, including motor vehicle traffic, which contribute to emissions which result in the alert threshold being exceeded. These may also include effective measures in relation to the use of industrial plants or products.3. When developing and implementing the short-term action plans, Member States shall consider examples of measures (the effectiveness of which has been assessed), which should be included in the guidance referred to in Article 12.4. Member States shall make available to the public and to appropriate organisations such as environmental organisations, consumer organisations, organisations representing the interests of sensitive population groups and other relevant health care bodies both the results of their investigations and the content of specific short-term action plans as well as information on the implementation of these plans.Article 8Transboundary pollution1. Where ozone concentrations exceeding target values or long-term objectives are due largely to precursor emissions in other Member States, the Member States concerned shall cooperate, where appropriate, in drawing up joint plans and programmes in order to attain the target values or long-term objectives, save where not achievable through proportionate measures. The Commission shall assist in those efforts. In carrying out its obligations under Article 11, the Commission shall consider, taking into account Directive 2001/81/EC, in particular Article 9 thereof, whether further action should be taken at Community level in order to reduce precursor emissions responsible for such transboundary ozone pollution.2. Member States shall, if appropriate according to Article 7, prepare and implement joint short-term action plans covering neighbouring zones in different Member States. Member States shall ensure that neighbouring zones in different Member States, which have developed short-term action plans, receive all appropriate information.3. Where exceedances of the information threshold or alert threshold occur in zones close to national borders, information should be provided as soon as possible to the competent authorities in the neighbouring Member States concerned in order to facilitate the provision of information to the public in those States.4. In drawing up the plans and programmes referred to in paragraph 1 and 2 and in informing the public as referred to in paragraph 3, Member States shall, where appropriate, pursue cooperation with third countries, with particular emphasis on accession candidate countries.Article 9Assessment of concentrations of ozone and precursor substances in ambient air1. In zones and agglomerations where, during any of the previous five years of measurement, concentrations of ozone have exceeded a long-term objective, fixed continuous measurement is mandatory.Where fewer than five years' data are available, Member States may, to determine exceedances, combine measurement campaigns of short duration at times and locations likely to be typical of the highest pollution levels with results obtained from emission inventories and modelling.Annex IV sets out criteria for determining the location of sampling points for the measurement of ozone.Section I of Annex V sets out the minimum number of fixed sampling points for continuous measurement of ozone in each zone or agglomeration within which measurement is the sole source of information for assessing air quality.Measurements of nitrogen dioxide shall also be made at a minimum of 50 % of the ozone sampling points required by Section I of Annex V. Measurement of nitrogen dioxide shall be continuous, except at rural background stations, as defined in section I of Annex IV, where other measurement methods may be used.For zones and agglomerations within which information from sampling points for fixed measurement is supplemented by information from modelling and/or indicative measurement, the total number of sampling points specified in Section I of Annex V may be reduced, provided that:(a) the supplementary methods provide an adequate level of information for the assessment of air quality with regard to target values, information and alert thresholds;(b) the number of sampling points to be installed and the spatial resolution of other techniques are sufficient for the concentration of ozone to be established in accordance with the data quality objectives specified in Section I of Annex VII and lead to assessment results as specified in Section II of Annex VII;(c) the number of sampling points in each zone or agglomeration amounts to at least one sampling point per two million inhabitants or one sampling point per 50000 km², whichever produces the greater number of sampling points;(d) each zone or agglomeration contains at least one sampling point, and(e) nitrogen dioxide is measured at all remaining sampling points except at rural background stations.In this case, the results of modelling and/or indicative measurement shall be taken into account for the assessment of air quality with respect to the target values.2. In zones and agglomerations where, during each of the previous five years of measurement, concentrations are below the long-term objectives, the number of continuous measurement stations shall be determined in accordance with Section II of Annex V.3. Each Member State shall ensure that at least one measuring station to supply data on concentrations of the ozone precursor substances listed in Annex VI is installed and operated in its territory. Each Member State shall choose the number and siting of the stations at which ozone precursor substances are to be measured, taking into account the objectives, methods and recommendations laid down in the said Annex.As part of the guidance developed under Article 12, guidelines for an appropriate strategy to measure ozone precursor substances shall be laid down, taking into account existing requirements in Community legislation and the cooperative programme for monitoring and evaluation of the long-range transmission of air pollutants in Europe (EMEP).4. Reference methods for analysis of ozone are set out in Section I of Annex VIII. Section II of Annex VIII provides for reference modelling techniques for ozone.5. Any amendments necessary to adapt this Article and Annexes IV to VIII to scientific and technical progress shall be adopted in accordance with the procedure laid down in Article 13(2).Article 10Transmission of information and reports1. When forwarding information to the Commission under Article 11 of Directive 96/62/EC, Member States shall also, and, for the first time, for the calendar year following the date referred to in Article 15(1):(a) send to the Commission for each calendar year no later than 30 September of the following year the lists of zones and agglomerations referred to in Article 3(2), Article 4(2) and Article 5;(b) send to the Commission a report giving an overview of the situation as regards exceedance of the target values as laid down in section II of Annex I. This report shall provide an explanation of annual exceedances of the target value for the protection of human health. The report shall also contain the plans and programmes referred to in Article 3(3). The report shall be sent no later than two years after the end of the period during which exceedances of the target values for ozone were observed;(c) inform the Commission every three years of the progress of any such plan or programme.2. Furthermore, Member States shall, for the first time, for the calendar year following the date referred to in Article 15(1):(a) for each month from April to September each year, send to the Commission, on a provisional basis,(i) by no later than the end of the following month, for each day with exceedance(s) of the information and/or the alert threshold, the following information: date, total hours of exceedance, maximum 1 h ozone value(s);(ii) by no later than 31 October each year, any other information specified in Annex III;(b) for each calendar year no later than 30 September of the following year, send to the Commission the validated information specified in Annex III and the annual average concentrations for that year of the ozone precursor substances specified in Annex VI;(c) forward to the Commission every three years, within the framework of the sectoral report referred to in Article 4 of Council Directive 91/692/EEC(11), and no later than 30 September following the end of each three-year period:(i) information reviewing the levels of ozone observed or assessed, as appropriate, in the zones and agglomerations referred to in Articles 3(2), Article 4(2) and Article 5;(ii) information on any measures taken or planned under Article 4(2), and(iii) information regarding decisions on short-term action plans and concerning the design and content, and an assessment of the effects, of any such plans prepared in accordance with Article 7.3. The Commission shall:(a) ensure that the information submitted pursuant to paragraph 2(a) is promptly made available by appropriate means and is transmitted to the European Environment Agency;(b) publish annually a list of the zones and agglomerations submitted pursuant to paragraph 1(a) and, by 30 November each year, a report on the ozone situation during the current summer and the preceding calendar year, aiming to provide overviews, in a comparable format, of each Member State's situation, taking into account the different meteorological conditions and transboundary pollution, and an overview of all the exceedances of the long-term objective in the Member States;(c) check regularly the implementation of the plans or programmes submitted pursuant to paragraph 1(b) by examining their progress and the trends in air pollution, taking account of meteorological conditions and the origin of the ozone precursors (biogenic or anthropogenic);(d) take into account the information provided under paragraphs 1 and 2 in preparing three-yearly reports on ambient air quality in accordance with Article 11(2) of Directive 96/62/EC;(e) arrange appropriate exchange of information and experience forwarded in accordance with paragraph 2(c)(iii) regarding the design and implementation of short-term action plans.4. When carrying out the tasks referred to in paragraph 3, the Commission shall, as necessary, call upon the expertise available in the European Environment Agency.5. The date by which Member States shall inform the Commission of the methods used for the preliminary assessment of air quality under Article 11(1)(d) of Directive 96/62/EC shall be no later than 9 September 2003.Article 11Review and reporting1. The Commission shall submit to the European Parliament and the Council by 31 December 2004, at the latest, a report based on experience of the application of this Directive. It shall report, in particular, on:(a) the findings of the most recent scientific research, in the light of the World Health Organisation's Guidelines, into the effects of exposure to ozone on the environment and human health, specifically taking into account sensitive population groups; the development of more accurate models shall be taken into account;(b) technological developments, including progress achieved in methods of measuring and otherwise assessing concentrations and evolution of ozone concentrations throughout Europe;(c) comparison of model predictions with actual measurements;(d) the setting of, and levels for, long-term objectives, for target values, for information and alert thresholds;(e) the results on the effects of ozone on crops and natural vegetation of the International Cooperative Programme under UN/ECE Convention on Long-range Transboundary Air Pollution.2. The report shall be presented as an integral part of an air quality strategy designed to review and propose Community air quality objectives and develop implementing strategies to ensure achievement of those objectives. In this context the report shall take into account:(a) the broad scope for making further reductions in polluting emissions across all relevant sources, taking account of technical feasibility and cost-effectiveness;(b) relationships between pollutants, and opportunities for combined strategies to achieve Community air quality and related objectives;(c) the potential for further action to be taken at Community level in order to reduce precursor emissions;(d) the progress in implementing the target values in Annex I, including the plans and programmes developed and implemented in accordance with Articles 3 and 4, the experience in implementing short-term action plans under Article 7 and the conditions, as laid down under Annex IV, under which air quality measurement has been carried out;(e) the potential to achieve the long-term objectives, set out in Section III of Annex I, within a specified time period;(f) current and future requirements for informing the public and for the exchange of information between Member States and the Commission;(g) the relationship between this Directive and expected changes resulting from measures to be taken by the Community and Member States in order to fulfil commitments relating to climate change;(h) transport of pollution across national boundaries taking account of measures taken in accession candidate countries.3. The report shall also include a review of the provisions of this Directive in the light of its findings and it shall be accompanied, if appropriate, by proposals to amend this Directive, paying special attention to the effects of ozone on the environment and on human health, with particular reference to sensitive population groups.Article 12Guidance1. The Commission shall develop guidance for implementing this Directive by 9 September 2002. In so doing, it will call upon the expertise available in the Member States, the European Environment Agency and other expert bodies, as appropriate and taking into account existing requirements in Community legislation and EMEP.2. The guidance shall be adopted in accordance with the procedure laid down in Article 13(2). Such guidance shall not have the effect of modifying the target values, long-term objectives, alert threshold or information threshold either directly or indirectly.Article 13Committee procedure1. The Commission shall be assisted by the committee established by Article 12(2) of Directive 96/62/EC.2. Where reference is made to this paragraph, Articles 5 and 7 of Decision 1999/468/EC shall apply, having regard to the provisions of Article 8 thereof.The period laid down in Article 5(6) of Decision 1999/468/EC shall be set at three months.3. The committee shall adopt its rules of procedure.Article 14PenaltiesMember States shall determine the penalties applicable to breaches of the national provisions adopted pursuant to this Directive. The penalties shall be effective, proportionate and dissuasive.Article 15Transposition1. Member States shall bring into force the laws, regulations and administrative provisions necessary to comply with this Directive by 9 September 2003.They shall forthwith inform the Commission thereof.When Member States adopt those measures, they shall contain a reference to this Directive or be accompanied by such a reference on the occasion of their official publication. Member States shall determine how such reference is to be made.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 16RepealDirective 92/72/EEC shall be repealed from 9 September 2003.Article 17Entry into forceThis Directive shall enter into force on the day of its publication in the Official Journal of the European Communities.Article 18AddresseesThis Directive is addressed to the Member States.Done at Brussels, 12 February 2002.For the European ParliamentThe PresidentP. CoxFor the CouncilThe PresidentJ. Piqué i Camps(1) OJ C 56 E, 29.2.2000, p. 40, andOJ C 29 E, 30.1.2001, p. 291.(2) OJ C 51, 23.2.2000, p. 11.(3) OJ C 317, 6.11.2000, p. 35.(4) Opinion of the European Parliament of 15 March 2000 (OJ C 377, 29.12.2000, p. 154), Council Common Position of 8 March 2001 (OJ C 126, 26.4.2001, p. 1) and Decision of the European Parliament of 13 June 2001 (not yet published in the Official Journal). Decision of the European Parliament of 17 January 2002 and Decision of the Council of 19 December 2001.(5) OJ C 138, 17.5.1993, p. 1.(6) OJ L 275, 10.10.1998, p. 1.(7) OJ L 296, 21.11.1996, p. 55.(8) OJ L 309, 27.11.2001, p. 22.(9) OJ L 184, 17.7.1999, p. 23.(10) OJ L 297, 13.10.1992, p. 1.(11) OJ L 377, 31.12.1991, p. 48.ANNEX IDEFINITIONS, TARGET VALUES AND LONG-TERM OBJECTIVES FOR OZONEI. DefinitionsAll values are to be expressed in µg/m³. The volume must be standardised at the following conditions of temperature and pressure: 293 K and 101,3 kPa. The time is to be specified in Central European Time.AOT40 (expressed in (µg/m³)·hours) means the sum of the difference between hourly concentrations greater than 80 µg/m³ (= 40 parts per billion) and 80 µg/m³ over a given period using only the 1 hour values measured between 8:00 and 20:00. Central European Time each day(1).In order to be valid, the annual data on exceedances used to check compliance with the target values and long-term objectives below must meet the criteria laid down in Section II of Annex III.II. Target values for ozone>TABLE>III. Long-term objectives for ozone>TABLE>(1) Or the appropriate time for ultra-peripheral regions.ANNEX IIINFORMATION AND ALERT THRESHOLDSI. Information and alert thresholds for ozone>TABLE>II. Minimum details to be supplied to the public when the information or alert threshold is exceeded or exceedance is predictedDetails to be supplied to the public on a sufficiently large scale as soon as possible should include:1. information on observed exceedance(s):- location or area of the exceedance,- type of threshold exceeded (information or alert),- start time and duration of the exceedance,- highest 1-hour and 8-hour mean concentration;2. forecast for the following afternoon/day(s):- geographical area of expected exceedances of information and/or alert threshold,- expected change in pollution (improvement, stabilisation or deterioration);3. information on type of population concerned, possible health effects and recommended conduct:- information on population groups at risk,- description of likely symptoms,- recommended precautions to be taken by the population concerned,- where to find further information;4. information on preventive action to reduce pollution and/or exposure to it:indication of main source sectors; recommendations for action to reduce emissions.ANNEX IIIInformation submitted by Member States to the Commission and criteria for aggregating data and calculating statistical parametersI. Information to be submitted to the CommissionThe following table stipulates the type and amount of data Member States are to submit to the Commission:>TABLE>As part of the yearly reporting, the following must also be provided, if all available hourly data for ozone, nitrogen dioxide and nitrogen oxides of the year in question have not already been delivered under the framework of Council Decision 97/101/EC(1):- for ozone, nitrogen dioxide, nitrogen oxides and the sums of ozone and nitrogen dioxide (added as parts per billion and expressed in µg/m³ ozone) the maximum, 99.9th, 98th, 50th percentile and annual average and number of valid data from hourly series,- the maximum, 98th, 50th percentile and annual average from series of daily 8-hour ozone maxima.Data submitted in the monthly reports are considered provisional and are to be updated, if necessary, in subsequent submissions.II. Criteria for aggregating data and calculating statistical parametersPercentiles are to be calculated using the method specified in Council Decision 97/101/EC.The following criteria are to be used for checking validity when aggregating data and calculating statistical parameters:>TABLE>(1) OJ L 35, 5.2.1997, p. 14.ANNEX IVCRITERIA FOR CLASSIFYING AND LOCATING SAMPLING POINTS FOR ASSESSMENTS OF OZONE CONCENTRATIONSThe following considerations apply to fixed measurements:I. Macroscale siting>TABLE>For rural and rural background stations, consideration should be given, where appropriate, to coordination with the monitoring requirements of Commission Regulation (EC) No 1091/94(1) concerning protection of the Community's forests against atmospheric pollution.II. Microscale sitingThe following guidelines should be followed, as far as practicable:1. The flow around the inlet sampling probe should be unrestricted (free in an arc of at least 270°) without any obstructions affecting the air flow in the vicinity of the sampler, i.e. away from buildings, balconies, trees and other obstacles by more than twice the height the obstacle protrudes above the sampler.2. In general, the inlet sampling point should be between 1.5 m (the breathing zone) and 4 m above the ground. Higher positions are possible for urban stations in some circumstances and in wooded areas.3. The inlet probe should be positioned well away from such sources as furnaces and incineration flues and more than 10 m from the nearest road, with distance increasing as a function of traffic intensity.4. The sampler's exhaust outlet should be positioned so as to avoid recirculation of exhaust air to the sampler inlet.The following factors may also be taken into account:1. interfering sources;2. security;3. access;4. availability of electrical power and telephone communications;5. visibility of the site in relation to its surroundings;6. safety of public and operators;7. the desirability of colocating sampling points for different pollutants;8. planning requirements.III. Documentation and review of site selectionSite selection procedures should be fully documented at the classification stage by such means as compass point photographs of the surroundings and a detailed map. Sites should be reviewed at regular intervals with repeated documentation to ensure that selection criteria are still being met.This requires proper screening and interpretation of the monitoring data in the context of the meteorological and photochemical processes affecting the ozone concentrations measured at the respective site.(1) OJ L 125, 18.5.1994, p. 1.ANNEX VCRITERIA FOR DETERMINING THE MINIMUM NUMBER OF SAMPLING POINTS FOR FIXED MEASUREMENT OF CONCENTRATIONS OF OZONEI. Minimum number of sampling points for fixed continuous measurements to assess air quality in view of compliance with the target values, long-term objectives and information and alert thresholds where continuous measurement is the sole source of information>TABLE>II. Minimum number of sampling points for fixed measurements for zones and agglomerations attaining the long-term objectivesThe number of sampling points for ozone must, in combination with other means of supplementary assessment such as air quality modelling and colocated nitrogen dioxide measurements, be sufficient to examine the trend of ozone pollution and check compliance with the long-term objectives. The number of stations located in agglomerations and other zones may be reduced to one-third of the number specified in Section I. Where information from fixed measurement stations is the sole source of information, at least one monitoring station should be kept. If, in zones where there is supplementary assessment, the result of this is that a zone has no remaining station, coordination with the number of stations in neighbouring zones must ensure adequate assessment of ozone concentrations against long-term objectives. The number of rural background stations should be 1 per 100000 km².ANNEX VIMEASUREMENTS OF OZONE PRECURSOR SUBSTANCESObjectivesThe main objectives of such measurements are to analyse any trend in ozone precursors, to check the efficiency of emission reduction strategies, to check the consistency of emission inventories and to help attribute emission sources to pollution concentration.An additional aim is to support the understanding of ozone formation and precursor dispersion processes, as well as the application of photochemical models.SubstancesMeasurement of ozone precursor substances must include at least nitrogen oxides, and appropriate volatile organic compounds (VOC). A list of volatile organic compounds recommended for measurement is given below.EthaneEthyleneAcetylenePropanePropenen-Butanei-Butane1-Butenetrans-2-Butenecis-2-Butene1.3-Butadienen-Pentanei-Pentane1-Pentene2-PenteneIsoprenen-Hexanei-Hexanen-Heptanen-Octanei-OctaneBenzeneTolueneEthyl benzenem+p-Xyleneo-Xylene1,2,4-Trimeth. benzene1,2,3-Trimeth. benzene1,3,5-Trimeth. benzeneFormaldehydeTotal non-methane hydrocarbonsReference methodsThe reference method specified in Directive 1999/30/CE(1) or in subsequent Community legislation will apply for nitrogen oxides.Each Member State must inform the Commission of the methods it uses to sample and measure VOC. The Commission must carry out inter-comparison exercises as soon as possible and investigate the potential for defining reference methods for precursor sampling and measurement in order to improve the comparability and precision of measurements for the review of this Directive in accordance with Article 11.SitingMeasurements should be taken in particular in urban and suburban areas at any monitoring site set up in accordance with the requirements of Directive 96/62/EC and considered appropriate with regard to the above monitoring objectives.(1) OJ L 163, 29.6.1999, p. 41.ANNEX VIIDATA QUALITY OBJECTIVES AND COMPILATION OF THE RESULTS OF AIR QUALITY ASSESMENTI. Data quality objectivesThe following data quality objectives, for allowed uncertainty of assessment methods, and of minimum time coverage and of data capture of measurement are provided to guide quality-assurance programmes.>TABLE>The uncertainty (on a 95 % confidence interval) of the measurement methods will be evaluated in accordance with the principles of the ISO "Guide to the Expression of Uncertainty in Measurement" (1993), or the methodology of ISO 5725-1 "Accuracy (trueness and precision) of measurement methods and results" (1994) or equivalent. The percentages for uncertainty in the table are given for individual measurements, averaged over the period for calculating target values and long-term objectives, for a 95 % confidence interval. The uncertainty for continuous fixed measurements should be interpreted as being applicable in the region of the concentration used for the appropriate threshold.The uncertainty for modelling and objective estimation is defined as the maximum deviation of the measured and calculated concentration levels, over the period for calculating the appropriate threshold, without taking into account the timing of the events."Time coverage" is defined as the percentage of the time considered for setting the threshold value during which the pollutant is measured."Data capture" is defined as the ratio of the time for which the instrument produces valid data, to the time for which the statistical parameter or aggregated value is to be calculated.The requirements for minimum data capture and time coverage do not include losses of data due to the regular calibration or normal maintenance of the instrumentation.II. Results of air quality assessmentThe following information should be compiled for zones or agglomerations within which sources other than measurement are employed to supplement information from measurement:- a description of the assessment activities carried out,- specific methods used, with references to descriptions of the method,- sources of data and information,- a description of results, including uncertainties and, in particular, the extent of any area within the zone or agglomeration over which concentrations exceed long-term objectives or target values,- for long-term objectives or target values whose object is the protection of human health, the population potentially exposed to concentrations in excess of the threshold.Where possible, Member States should compile maps showing concentration distributions within each zone and agglomeration.III. StandardisationFor ozone the volume must be standardised at the following conditions of temperature and pressure: 293 K, 101,3 kPa. For nitrogen oxides the standardisation specified in Directive 1999/30/EC will apply.ANNEX VIIIREFERENCE METHOD FOR ANALYSIS OF OZONE AND CALIBRATION OF OZONE INSTRUMENTSI. Reference method for analysis of ozone and calibration of ozone instruments- Analysis method: UV photometric method (ISO FDIS 13964),- Calibration method: Reference UV photometer (ISO FDIS 13964, VDI 2468, B1.6).This method is being standardised by the European Committee for Standardisation (CEN). Once the latter has published the relevant standard, the method and techniques described therein will constitute the reference and calibration method in this Directive.A Member State may also use any other method which it can demonstrate gives results equivalent to the above method.II. Reference modelling technique for ozoneReference modelling techniques cannot be specified at present. Any amendments to adapt this point to scientific and technical progress will be adopted in accordance with the procedure laid down in Article 13(2).


Avis juridique important

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31976L0933

Sixteenth Commission Directive 76/933/EEC of 1 December 1976 amending the Annexes to Council Directive 70/524/EEC of 23 November 1970 concerning additives in feedingstuffs

Official Journal L 364 , 31/12/1976 P. 0018 - 0019 Greek special edition: Chapter 03 Volume 16 P. 0209

++++SIXTEENTH COMMISSION DIRECTIVE  OF 1 DECEMBER 1976  AMENDING THE ANNEXES TO COUNCIL DIRECTIVE 70/524/EEC OF 23 NOVEMBER 1970 CONCERNING ADDITIVES IN FEEDINGSTUFFS   ( 76/933/EEC )  THE COMMISSION OF THE EUROPEAN COMMUNITIES ,  HAVING REGARD TO THE TREATY ESTABLISHING THE EUROPEAN ECONOMIC COMMUNITY ,  HAVING REGARD TO THE COUNCIL DIRECTIVE OF 23 NOVEMBER 1970 CONCERNING ADDITIVES IN FEEDINGSTUFFS ( 1 ) , AS LAST AMENDED BY THE FIFTEENTH COMMISSION DIRECTIVE OF 21 JUNE 1976 ( 2 ) , AND IN PARTICULAR ARTICLE 6 THEREOF ,  WHEREAS THE ABOVEMENTIONED DIRECTIVE PROVIDES FOR THE CONTENT OF THE ANNEXES TO BE SUBJECT TO CONSTANT REVISION IN THE LIGHT OF THE DEVELOPMENT OF SCIENTIFIC AND TECHNICAL KNOWLEDGE ;  WHEREAS RESEARCH CARRIED OUT AT COMMUNITY LEVEL HAS SHOWN THAT THE MAXIMUM LEVELS LAID DOWN IN ANNEX I FOR VITAMIN D3 IN POULTRY FEEDINGSTUFFS ARE INSUFFICIENT TO MEET THE NEEDS OF THESE SPECIES ; WHEREAS IT IS DESIRABLE TO AUTHORIZE IN THIS CASE HIGHER MAXIMUM LEVELS TO THE EXTENT THAT NO RISK TO ANIMAL OR HUMAN HEALTH RESULTS THEREFROM ;  WHEREAS THE USE OF THE GROWTH PROMOTER OLAQUINDOX FOR SWINE HAS BEEN SUCCESSFULLY TESTED IN CERTAIN MEMBER STATES ; WHEREAS IT IS DESIRABLE TO AUTHORIZE ITS USE , SUBJECT TO CERTAIN CONDITIONS , AT LEAST NATIONAL LEVEL UNTIL IT IS PERMITTED AT COMMUNITY LEVEL ;  WHEREAS THE MEASURES PROVIDED FOR IN THIS DIRECTIVE ARE IN ACCORDANCE WITH THE OPINION OF THE STANDING COMMITTEE FOR FEEDINGSTUFFS ,  HAS ADOPTED THIS DIRECTIVE :  ARTICLE 1  THE ANNEXES TO THE COUNCIL DIRECTIVE OF 23 NOVEMBER 1970 CONCERNING ADDITIVES IN FEEDINGSTUFFS SHALL BE AMENDED AS SPECIFIED IN THE FOLLOWING ARTICLES .  ARTICLE 2  ANNEX I , PART H " VITAMINS , PROVITAMINS AND CHEMICALLY WELL DEFINED SUBSTANCES HAVING A SIMILAR EFFECT " SHALL BE AMENDED IN RELATION TO ADDITIVE NO E 671 " VITAMIN D3 " AS FOLLOWS :  1 . THE WORDS " LAYING HENS " IN THE COLUMN HEADED  " SPECIES OF ANIMAL " , AS WELL AS THE FIGURE " 3 000 " APPEARING FOR THIS SPECIES IN THE COLUMN HEADED  " MAXIMUM CONTENT I.U./KG OF COMPLETE FEEDINGSTUFFS OR OF THE DAILY RATION " SHALL BE REPLACED BY THE WORDS " CHICKENS FOR FATTENING , TURKEYS " AND BY THE FIGURE " 5 000 " ;  2 . THE FIGURE " 2 000 " APPEARING IN THE COLUMN HEADED " MAXIMUM CONTENT I.U./KG OF COMPLETE FEEDINGSTUFFS OR OF THE DAILY RATION " IN RESPECT OF THE SPECIES " OTHER POULTRY " SHALL BE REPLACED BY THE FIGURE " 3 000 " .  ARTICLE 3  THE FOLLOWING ITEM SHALL BE ADDED TO ANNEX II , PART F " GROWTH PROMOTERS " :  NO*ADDITIVE*CHEMICAL FORMULA , DESCRIPTION*SPECIES OF ANIMAL*MAXIMUM AGE*PPM OF COMPLETE FEEDINGSTUFFS*OTHER PROVISIONS*PERIOD OF AUTHORIZATION*  *****MINIMUM CONTENT*MAXIMUM CONTENT***  3*OLAQUINDOX*2-(N-2'-HYDROXYATHYL-CARBAMOYL ) 3-METHYL-QUINOXALINE-1,4-DIOXIDE*SWINE*FOUR MONTHS*15*50*USE PROHIBITED AT LEAST FOUR WEEKS BEFORE SLAUGHTER*31 DECEMBER 1978*  *******MIXING OR SIMULTANEOUS USE WITH ANTIBIOTICS PROHIBITED**  *****50*100*MILK FEEDS ONLY**  ARTICLE 4  THE MEMBER STATES SHALL , NOT LATER THAN 1 FEBRUARY 1977 , BRING INTO FORCE THE LAWS , REGULATIONS OR ADMINISTRATIVE PROVISIONS NECESSARY TO COMPLY WITH THIS DIRECTIVE . THEY SHALL FORTHWITH INFORM THE COMMISSION THEREOF .  ARTICLE 5  THIS DIRECTIVE IS ADDRESSED TO THE MEMBER STATES .  DONE AT BRUSSELS , 1 DECEMBER 1976 .  FOR THE COMMISSION  P . J . LARDINOIS  MEMBER OF THE COMMISSION  ( 1 ) OJ NO L 270 , 14 . 12 . 1970 , P . 1 .  ( 2 ) OJ NO L 198 , 23 . 7 . 1976 , P . 10 .