Council Directive 70/220/EEC of 20 March 1970 on the approximation of the laws of the Member States relating to measures to be taken against air pollution by gases from positive-ignition engines of motor vehicles
Modified by
  • Actconcerning the Conditions of Accession and the Adjustments to the Treaties, 172B, March 27, 1972
  • Council Directiveof 28 May 1974adapting to technical progress Council Directive No 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by gases from positive-ignition engines of motor vehicles(74/290/EEC), 374L0290, June 15, 1974
  • Commission Directiveof 30 November 1976adapting to technical progress Council Directive 70/220/EEC of 20 March 1970 on the approximation of the laws of the Member States relating to measures to be taken against air pollution by gases from positive-ignition engines of motor vehicles(77/102/EEC), 377L0102, February 3, 1977
  • Commission Directiveof 14 July 1978adapting to technical progress Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against pollution of the air by gases from positive ignition engines installed in motor vehicles(78/665/EEC), 378L0665, August 14, 1978
  • Council Directiveof 16 June 1983amending Council Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by gases from positive-ignition engines of motor vehicles(83/351/EEC), 383L0351, July 20, 1983
  • Council Directiveof 3 December 1987amending Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by gases from the engines of motor vehicles(88/76/EEC), 388L0076, February 9, 1988
  • Council Directiveof 16 June 1988amending Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by gases from engines of motor vehicles (Restriction of particulate pollutant emissions from diesel engines)(88/436/EEC) Corrigendum to Council Directive 88/436/EEC of 16 June 1988 amending Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by gases from engines of motor vehicles (Restriction of particulate pollutant emissions from diesel engines)(Official Journal of the European Communities No L 214 of 6 August 1988), 388L0436388L0436R(01), August 6, 1988
  • Council Directiveof 18 July 1989amending with regard to European emission standards for cars below 1,4 litres, Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by emissions from motor vehicles(89/458/EEC) Corrigendum to Council Directive 89/458/EEC of 18 July 1989 amending with regard to European emission standards for cars below 1,4 litres, Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by emissions from motor vehicles(Official Journal of the European Communities No L 226 of 3 August 1989), 389L0458389L0458R(01), August 3, 1989
  • Commission Directiveof 17 July 1989adapting to technical progress Council Directives 70/157/EEC, 70/220/EEC, 72/245/EEC, 72/306/EEC, 80/1268/EEC and 80/1269/EEC relating to motor vehicles(89/491/EEC), 389L0491, August 15, 1989
  • Council Directiveof 26 June 1991amending Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by emissions from motor vehicles(91/441/EEC), 391L0441, August 30, 1991
  • Council Directive 93/59/EECof 28 June 1993amending Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by emissions from motor vehicles, 393L0059, July 28, 1993
  • Directive 94/12/EC of the European Parliament and the Councilof 23 March 1994relating to measures to be taken against air pollution by emissions from motor vehicles and amending Directive 70/220/EEC, 394L0012, April 19, 1994
  • Commission Directive 96/44/ECof 1 July 1996adapting to technical progress Council Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by emissions from motor vehicles(Text with EEA relevance), 396L0044, August 20, 1996
  • Directive 96/69/EC of the European Parliament and of the Councilof 8 October 1996amending Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by emissions from motor vehicles, 396L0069, November 1, 1996
  • Commission Directive 98/77/ECof 2 October 1998adapting to technical progress Council Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by emissions from motor vehicles(Text with EEA relevance), 398L0077, October 23, 1998
  • Directive 98/69/EC of the European Parliament and of the Councilof 13 October 1998relating to measures to be taken against air pollution by emissions from motor vehicles and amending Council Directive 70/220/EEC Corrigendum to Directive 98/69/EC of the European Parliament and of the Council of 13 October 1998 relating to measures to be taken against air pollution by emissions from motor vehicles and amending Council Directive 70/220/EEC(Official Journal of the European Communities L 350 of 28 December 1998) Corrigendum to Directive 98/69/EC of the European Parliament and of the Council of 13 October 1998 relating to measures to be taken against air pollution by emissions from motor vehicles and amending Council Directive 70/220/EEC(Official Journal of the European Communities L 350 of 28 december 1998), 398L0069398L0069R(01)398L0069R(02), December 28, 1998
  • Commission Directive 1999/102/ECof 15 December 1999adapting to technical progress Council Directive 70/220/EEC relating to measures to be taken against air pollution by emissions from motor vehicles(Text with EEA relevance), 399L0102, December 28, 1999
  • Directive 2001/1/EC of the European Parliament and of the Councilof 22 January 2001amending Council Directive 70/220/EEC concerning measures to be taken against air pollution by emissions from motor vehicles, 301L0001, February 6, 2001
  • Directive 2001/100/EC of the European Parliament and of the Councilof 7 December 2001amending Council Directive 70/220/EEC on the approximation of the laws of the Member States on measures to be taken against air pollution by emissions from motor vehicles(Text with EEA relevance), 301L0100, January 18, 2002
  • Commission Directive 2002/80/ECof 3 October 2002adapting to technical progress Council Directive 70/220/EEC relating to measures to be taken against air pollution by emissions from motor vehicles(Text with EEA relevance), 302L0080, October 28, 2002
  • Commission Directive 2003/76/ECof 11 August 2003amending Council Directive 70/220/EEC relating to measures to be taken against air pollution by emissions from motor vehicles(Text with EEA relevance), 303L0076, August 15, 2003
  • Actconcerning the conditions of accession of the Czech Republic, the Republic of Estonia, the Republic of Cyprus, the Republic of Latvia, the Republic of Lithuania, the Republic of Hungary, the Republic of Malta, the Republic of Poland, the Republic of Slovenia and the Slovak Republic and the adjustments to the Treaties on which the European Union is founded, 103T, September 23, 2003
  • Council Directive 2006/96/ECof 20 November 2006adapting certain Directives in the field of free movement of goods, by reason of the accession of Bulgaria and Romania, 306L0096, December 20, 2006
Corrected by
  • Corrigendum to Council Directive 88/436/EEC of 16 June 1988 amending Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by gases from engines of motor vehicles (Restriction of particulate pollutant emissions from diesel engines), 388L0436R(01), November 8, 1988
  • Corrigendum to Council Directive 89/458/EEC of 18 July 1989 amending with regard to European emission standards for cars below 1,4 litres, Directive 70/220/EEC on the approximation of the laws of the Member States relating to measures to be taken against air pollution by emissions from motor vehicles, 389L0458R(01), September 19, 1989
  • Corrigendum to Directive 98/69/EC of the European Parliament and of the Council of 13 October 1998 relating to measures to be taken against air pollution by emissions from motor vehicles and amending Council Directive 70/220/EEC, 398L0069R(01), April 21, 1999
  • Corrigendum to Directive 98/69/EC of the European Parliament and of the Council of 13 October 1998 relating to measures to be taken against air pollution by emissions from motor vehicles and amending Council Directive 70/220/EEC, 398L0069R(02), April 21, 1999
Council Directiveof 20 March 1970on the approximation of the laws of the Member States on measures to be taken against air pollution by emissions from motor vehicles (70/220/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 ParliamentOJ No C 160, 18.12.1969, p. 7.; Having regard to the Opinion of the Economic and Social CommitteeOJ No C 48, 16.4.1969, p. 16.; Whereas a regulation of 14 October 1968 amending the Straßenverkehrs-Zulassungs-Ordnung was published in Germany in the Bundesgesetzblatt Part I of 18 October 1968; whereas that regulation contains provisions on measures to be taken against air pollution by positive-ignition engines of motor vehicles; whereas those provisions will enter into force on 1 October 1970; Whereas a regulation of 31 March 1969 on the "Composition of exhaust gases emitted from petrol engines of motor vehicles" was published in France in the Journal officiel of 17 May 1969; whereas that regulation is applicable: from 1 September 1971, to type-approved vehicles with a new type of engine, that is to say, a type of engine which has never before been installed in a type-approved vehicle; from 1 September 1972, to vehicles put into service for the first time; Whereas those provisions are liable to hinder the establishment and proper functioning of the common market; whereas it is therefore necessary that all Member States adopt the same requirements, either in addition to or in place of their existing rules, in order, in particular, to allow the EEC type — approval procedure which was the subject of the Council DirectiveOJ No L 42, 23.2.1970, p. 1. 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 to be applied in respect of each type of vehicle; Whereas, however, the present Directive will be applied before the date laid down for the application of the Directive of 6 February 1970; whereas at that time therefore the procedures of this last Directive will not yet be applicable; whereas therefore an ad hoc procedure must be laid down in the form of a communication certifying that a vehicle type has been tested and that it satisfies the requirements of this Directive; Whereas, on the basis of that communication, each Member State requested to grant national type approval of a type of vehicle must be able to ascertain whether that type has been submitted to the tests laid down in this Directive; whereas, to this end, each Member State should inform the other Member States of its findings by sending them a copy of the communication completed for each type of motor vehicle which has been tested; Whereas a longer period of adaptation should be laid down for industry in respect of the requirements relating to the testing of the average emission of gaseous pollutants in a congested urban area after a cold start than in respect of the other technical requirements of this Directive; Whereas it is desirable to use the technical requirements adopted by the UN Economic Commission for Europe in its Regulation No 15ECE (Geneva) Document W/TRANS/WP 29/293/Rev. 1, 11.4.1969. (Uniform provisions concerning the approval of vehicles equipped with a positive-ignition engine with regard to the emission of gaseous pollutants by the engine), annexed to the Agreement of 20 March 1958 concerning the adoption of uniform conditions of approval and reciprocal recognition of approval for motor vehicle equipment and parts; Whereas, furthermore, the technical requirements must be rapidly adapted to take account of technical progress; whereas, to this end, provision should be made for application of the procedure laid down in Article 13 of the Council Directive of 6 February 1970 on the type approval of motor vehicles and their trailers; HAS ADOPTED THIS DIRECTIVE:
Article 1 For the purposes of this Directive: (a)"vehicle" means any vehicle as defined in Annex II Section A to Directive 70/156/EEC; (b)"a vehicle fuelled by LPG or NG" means a vehicle fitted with specific equipment for the use of LPG or NG in its propulsion system. Such an LPG or NG vehicle can be designed and constructed as a mono-fuel vehicle or a bi-fuel vehicle; (c)"a mono-fuel vehicle" means a vehicle that is designed primarily for permanent running on LPG or NG but may also have a petrol system for emergency purposes or starting only, where the petrol tank does not contain more than 15 litres of petrol; (d)"a bi-fuel vehicle" means a vehicle that can run part-time on petrol and also part-time on either LPG or NG.
Article 2 No Member State may refuse to grant EEC type approval or national type approval of a vehicle on grounds relating to air pollution by gases from positive-ignition engines of motor vehicles: from 1 October 1970, where that vehicle satisfies both the requirements contained in Annex I, with the exception of those in items 3.2.1.1 and 3.2.2.1, and the requirements contained in Annexes II, IV, V and VI; from 1 October 1971, where that vehicle satisfies, in addition, the requirements contained in items 3.2.1.1 and 3.2.2.1 of Annex I and in Annex III.
Article 2a No Member State may refuse or prohibit the sale or registration, entry into service or use of a vehicle on grounds relating to air pollution by gases from positive-ignition engines of motor vehicles if that vehicle satisfies the requirements set out in Annexes I, II, III, IV, V and VI.
Article 3 1. On application being made by a manufacturer or his authorised representative, the competent authorities of the Member State concerned shall complete the sections of the communication provided for in Annex VII. A copy of that communication shall be sent to the other Member States and to the applicant. Other Member States which are requested to grant national type approval for the same type of vehicle shall accept that document as proof that the tests provided for have been carried out. 2. The provisions of paragraph 1 shall be revoked as soon as the Council Directive of 6 February 1970 on the type approval of motor vehicles and their trailers enters into force.
Article 4 The Member State which has granted type approval shall take the necessary measures to ensure that it is informed of any modification of a part or characteristic referred to in item 1.1 of Annex I. The competent authorities of that Member State shall determine whether fresh tests should be carried out on the modified prototype and whether a fresh report should be drawn up. Where such tests reveal failure to comply with the requirements of this Directive, the modification shall not be approved.
Article 5 The amendments necessary for adjusting the requirements of Annexes I to XI so as to take account of technical progress shall be adopted in accordance with the procedure laid down in Article 13 of the Council Directive of 6 February 1970 on the type approval of motor vehicles and their trailers.
Article 6 1. Member States shall adopt provisions containing the requirements needed in order to comply with this Directive before 30 June 1970 and shall forthwith inform the Commission thereof. 2. Member States shall ensure that they communicate to the Commission the text of the main provisions of national law which they adopt in the field covered by this Directive.
Article 7 This Directive is addressed to the Member States.
null LIST OF ANNEXES
ANNEX I: Scope, definitions, application for EC type-approval, granting of EC type-approval, requirements and tests, extension of EC type-approval, conformity of production and in-service vehicles, on-board diagnostic (OBD) systems
Appendix 1: Verification of production conformity(1st statistical method)
Appendix 2: Verification of production conformity(2nd statistical method)
Appendix 3: In-service conformity check
Appendix 4: Statistical procedure for in-service conformity testing
ANNEX II: Information document
Appendix: Information on text conditions
ANNEX III: Type I test (verifying the average tailpipe emissions after a cold start)
Appendix 1: Operating cycle used for the type I test
Appendix 2: Chassis dynamometer
Appendix 3: Measurement method on the road-simulation on a chassis dynamometer
Appendix 4: Verification of inertias other than mechanical
Appendix 5: Description of tailpipe emission-sampling systems
Appendix 6: Method of calibrating the equipment
Appendix 7: Total system verification
Appendix 8: Calculation of the emission of pollutants
ANNEX IV: Type II test (carbon monoxide emission test at idling speed)
ANNEX V: Type III test (verifying emissions of crankcase gases)
ANNEX VI: Type IV test (determination of evaporative emissions from vehicles with positive-ignition engines)
Appendix 1: Calibration frequency and methods
Appendix 2: Diurnal ambient temperature profile for the diurnal emission test
ANNEX VII: Type VI test: Verifying the average low ambient temperature carbon monoxide and hydrocarbon tailpipe emissions after a cold start
ANNEX VIII: Type V test (ageing test for verifying the durability of anti-pollution devices)
ANNEX IX: Specifications of reference fuels
ANNEX IX a: Specifications of gaseous reference fuels
ANNEX X: Model EC type-approval certificate
Appendix: Addendum to EC information document
ANNEX XI: On-board-diagnostics (OBD) for motor vehicles
Appendix 1: Functional aspects of OBD systems
Appendix 2: Essential characteristics of the vehicle family
ANNEX XII: EC type-approval for a vehicle fuelled by LPG or natural gas with regards to its emissions
ANNEX XIII: EC type-approval of replacement catalytic converter as separate technical unit
Appendix 1: Information document
Appendix 2: EC type-approval certificate
Appendix 3: EC type-approval mark
ANNEX I SCOPE, DEFINITIONS, APPLICATION FOR EC TYPE-APPROVAL, GRANTING OF EC TYPE-APPROVAL, REQUIREMENTS AND TESTS, EXTENSION OF EC TYPE-APPROVAL, CONFORMITY OF PRODUCTION AND IN-SERVICE VEHICLES, ON-BOARD DIAGNOSTIC (OBD) SYSTEMS 1.SCOPE This Directive applies to tailpipe emissions at normal and low ambient temperature, evaporative emissions, emissions of crankcase gases, the durability of anti-pollution devices and on-board diagnostic (OBD) systems of motor vehicles equipped with positive-ignition engines,and tailpipe emissions, the durability of anti-pollution devices and on-board diagnostic (OBD) systems of vehicles of category M1 and N1As defined in Part A of Annex II to Directive 70/156/EEC., equipped with compression-ignition engines, covered by Article 1 of Directive 70/220/EEC in the version of Directive 83/351/EEC, with the exception of those vehicles of categories N1 for which type-approval has been granted pursuant to Directive 88/77/EECOJ L 36, 9.2.1998, p. 33.. At the request of the manufacturers, type-approval pursuant to this Directive may be extended from M1 or N1 vehicles equipped with compression ignition engines which have already been type-approved, to M2 and N2 vehicles having a reference mass not exceeding 2840 kg and meeting the conditions of section 6 of this Annex (extension of EEC type-approval). This Directive also applies to the EC type-approval procedure for replacement catalytic converters as separate technical units intended to be fitted on vehicles of category M1 and N1. 2.DEFINITIONS For the purposes of this Directive: 2.1. "Vehicle type" with regard to the tailpipe emissions from the engine, means a category of power-driven vehicles which do not differ in such essential respects as: 2.1.1. the equivalent inertia determined in relation to the reference mass as prescribed in section 5.1 of Annex III; and 2.1.2. the engine and vehicle characteristics as defined in Annex II. 2.2. "Reference mass" means the mass of the vehicle in running order less the uniform mass of the driver of 75 kg and increased by a uniform mass of 100 kg. 2.2.1. "Mass of the vehicle in running order" means the mass defined in section 2.6 of Annex I to Directive 70/156/EEC. 2.3. "Maximum mass" means the mass defined in section 2.7 of Annex I to Directive 70/156/EEC. 2.4. "Gaseous pollutants" means the exhaust gas emissions of carbon monoxide, oxides of nitrogen, expressed in nitrogen dioxide (NO2) equivalent, and hydrocarbons assuming ratio of: C1H1.85 for petrol, C1H1.86 for diesel, C1H2.525 for LPG, CH4 for NG. 2.5. "Particulate pollutants" means components of the exhaust gas which are removed from the diluted exhaust gas at a maximum temperature of 325 K (52 °C) by means of the filters described in Annex III. 2.6. "Tailpipe emissions" means: for positive-ignition engines, the emission of gaseous pollutants, for compression-ignition engines, the emission of gaseous and particulate pollutants. 2.7. "Evaporative emissions" means the hydrocarbon vapours lost from the fuel system of a motor vehicle other than those from tailpipe emissions. 2.7.1. "Tank breathing losses" are hydrocarbon emissions caused by temperature changes in the fuel tank (assuming a ratio of C1H2,33). 2.7.2. "Hot soak losses" are hydrocarbon emissions arising from the fuel system of a stationary vehicle after a period of driving (assuming a ratio of C1H2,20). 2.8. "Engine crankcase" means the spaces in, or external to, an engine which are connected to the oil sump by internal or external ducts through which gases and vapours can escape. 2.9. "Cold start device" means a device which temporarily enriches the air/fuel mixture of the engine thus assisting the engine to start. 2.10. "Starting aid" means a device which assists the engine to start without enrichment of the air/fuel mixture of the engine, e.g. glow plugs, modifications to the injection timing. 2.11. "Engine capacity" means: 2.11.1. for reciprocating piston engines, the nominal engine swept volume, 2.11.2. for rotary piston (Wankel) engines, double the nominal engine swept volume. 2.12. "Anti-pollution device" means those components of a vehicle that control and/or limit tailpipe and evaporative emissions. 2.13. "OBD" an on-board diagnostic system for emission control which has the capability of identifying the likely area of malfunction by means of fault codes stored in computer memory. 2.14. "In-service test" means the test and evaluation of conformity conducted in accordance with section 7.1.7 of this Annex. 2.15. "Properly maintained and used" means, for the purpose of a test vehicle, that such a vehicle satisfies the criteria for acceptance of a selected vehicle laid down in section 2 of Appendix 3 to this Annex. 2.16. "Defeat device" means any element of design which senses temperature, vehicle speed, engine RPM, transmission gear, manifold vacuum or any other parameter for the purpose of activating, modulating, delaying or deactivating the operation of any part of the emission control system, that reduces the effectiveness of the emission control system under conditions which may reasonably be expected to be encountered in normal vehicle operation and use. Such an element of design may not be considered a defeat device if: I.the need for the device is justified in terms of protecting the engine against damage or accident and for safe operation of the vehicle, or II.the device does not function beyond the requirements of engine starting, or III.conditions are substantially included in the Type I or Type VI test procedures. 2.17. "Original equipment catalytic converter", means a catalytic converter or an assembly of catalytic converters covered by the type-approval delivered for the vehicle and which are indicated in point 1.10 of the Appendix to Annex X to this Directive. 2.18. "Replacement catalytic converter" means a catalytic converter or an assembly of catalytic converters intended to replace an original equipment catalytic converter on a vehicle approved according to Directive 70/220/EEC which can be approved as a separate technical unit as defined in Article 4(1)(d) of Directive 70/156/EEC. 2.19. "Original replacement catalytic converter" means a catalytic converter or an assembly of catalytic converters whose types are indicated in point 1.10 of the Appendix to Annex X to this Directive but are offered on the market as separate technical units by the holder of the vehicle type-approval. 2.20. "Family of vehicles" means a group of vehicle types identified by a parent vehicle for the purpose of Annex XII. 2.21. "Fuel requirement by the engine" means the type of fuel normally used by the engine: petrol, LPG (liquefied petroleum gas), NG (natural gas), both petrol and LPG, both petrol and NG, diesel fuel. 3.APPLICATION FOR EC TYPE-APPROVAL 3.1. The application for EC type-approval pursuant to Article 3 (4) of Directive 70/156/EEC of a vehicle type with regard to its tailpipe emissions, evaporative emissions, durability of anti-pollution devices as well as to its on-board diagnostic (OBD) system must be submitted by the vehicle manufacturer.Should the application concern an on-board diagnostic (OBD) system the procedure described in Annex XI, section 3 must be followed. 3.1.1. Should the application concern an on-board diagnostic (OBD) system, it must be accompanied by the additional information required in section 3.2.12.2.8 of Annex II together with: 3.1.1.1. a declaration by the manufacturer of: 3.1.1.1.1. in the case of vehicles equipped with positive-ignition engines, the percentage of misfires out of a total number of firing events that would result in emissions exceeding the limits given in section 3.3.2 of Annex XI if that percentage of misfire had been present from the start of a type I test as described in section 5.3.1 of Annex III; 3.1.1.1.2. in the case of vehicles equipped with positive-ignition engines, the percentage of misfires out of a total number of firing events that could lead to an exhaust catalyst, or catalysts, overheating prior to causing irreversible damage; 3.1.1.2. detailed written information fully describing the functional operation characteristics of the OBD system, including a listing of all relevant parts of the vehicle's emission control system, i. e. sensors, actuators and components, that are monitored by the OBD system; 3.1.1.3. a description of the malfunction indicator (MI) used by the OBD system to signal the presence of a fault to a driver of the vehicle; 3.1.1.4. the manufacturer must describe provisions taken to prevent tampering with and modification of the emission control computer; 3.1.1.5. when appropriate, copies of other type-approvals with the relevant data to enable extensions of approvals; 3.1.1.6. if applicable, the particulars of the vehicle family as referred to in Annex XI, Appendix 2. 3.1.2. For the tests described in section 3 of Annex XI, a vehicle representative of the vehicle type or vehicle family fitted with the OBD system to be approved must be submitted to the technical service responsible for the type-approval test. If the technical service determines that the submitted vehicle does not fully represent the vehicle type or vehicle family described in Annex XI, Appendix 2, an alternative and if necessary an additional vehicle must be submitted for test in accordance with section 3 of Annex XI. 3.2. A model of the information document relating to tailpipe emissions, evaporative emissions, durability and the on-board diagnostic (OBD) system is given in Annex II. The information listed under section 3.2.12.2.8.6 of Annex II is to be included in Appendix 2 "OBD related information" to the EC type-approval certificate given in Annex X. 3.2.1. Where appropriate, copies of other type-approvals with the relevant data to enable extension of approvals and establishment of deterioration factors must be submitted. 3.3. For the tests described in Section 5 of this Annex a vehicle representative of the vehicle type to be approved must be submitted to the technical service responsible for the type-approval tests. 4.GRANTING OF EC TYPE-APPROVAL 4.1. If the relevant requirements are satisfied, EC type-approval is granted pursuant to Article 4 (3) of Directive 70/156/EEC. 4.2. A model of the EC type-approval certificate relating to tailpipe emissions, evaporative emissions, durability and the on-board diagnostic (OBD) system is given in Annex X. 4.3. An approval number in accordance with Annex VII to Directive 70/156/EEC shall be assigned to each type of vehicle approved. The same Member State shall not assign the same number to another type of vehicle. 5.REQUIREMENTS AND TESTS Note: As an alternative to the requirements of this section, vehicle manufacturers whose world-wide annual production is less than 10000 units may obtain EC type-approval on the basis of the corresponding technical requirements in: the California Code of Regulations, Title 13, Sections 1960.1 (f) (2) or (g) (1) and (g) (2), 1960.1 (p) applicable to 1996 and later model year vehicles, 1968.1, 1976 and 1975, applicable to 1995 and later model year light-duty vehicles, published by Barclay's Publishing.The type-approval authority must inform the Commission of the circumstances of each approval granted under this provision. 5.1.General 5.1.1. The components liable to effect tailpipe and evaporative emissions must be so designed, constructed and assembled as to enable the vehicle, in normal use, to comply with the requirements of this Directive, despite the vibration to which they may be subjected. The technical measures taken by the manufacturer must be such as to unsure that the tailpipe and evaporative emissions are effectively limited, pursuant to this Directive, throughout the normal life of the vehicle and under normal conditions of use. This will include the security of those hoses and their joints and connections, used within the emission control systems, which must be so constructed as to conform with the original design intent.For tailpipe emissions, these provisions are deemed to be met if the provisions of sections 5.3.1.4 (type-approval) and section 7 (conformity of production and in-service vehicles) respectively are complied with.For evaporative emissions, these provisions are deemed to be met if the provisions of section 5.3.4 (type-approval) and section 7 (conformity of production) are complied with. The use of a defeat device is prohibited. 5.1.2. Inlet orifices of petrol tanks: 5.1.2.1. Subject to 5.1.2.2, the inlet orifice of the fuel tank must be so designed that it prevents the tank from being filled from a petrol pump delivery nozzle which has an external diameter of 23,6 mm or greater. 5.1.2.2. Section 5.1.2.1 does not apply to a vehicle in respect of which both of the following conditions are satisfied, that is to say: 5.1.2.2.1. that the vehicle is so designed and constructed that no device designed to control the emission of gaseous pollutants is adversely affected by leaded petrol, and 5.1.2.2.2. that the vehicle is conspicuously, legibly and indelibly marked with the symbol for unleaded petrol specified in ISO 2575-1982 in a position immediately visible to a person filling the fuel tank. Additional markings are permitted. 5.1.3. Provision must be made to prevent excess evaporative emissions and fuel spillage caused by a missing fuel filler cap. This may be achieved by using one of the following: an automatically opening and closing, non-removable fuel filler cap, design features which avoid excess evaporative emissions in the case of a missing fuel filler cap, any other provision which has the same effect. Examples may include, but are not limited to, a tethered filler cap, a chained filler cap ore one utilizing the same locking key for the filler cap as for the vehicle's ignition. In this case the key must be removable from the filler cap only in the locked condition. 5.1.4.Provisions for electronic system security 5.1.4.1. Any vehicle with an emission control computer must include features to deter modification, except as authorised by the manufacturer. The manufacturer shall authorise modifications if these modifications are necessary for the diagnosis, servicing, inspection, retrofitting or repair of the vehicle. Any reprogrammable computer codes or operating parameters must be resistant to tampering and afford a level of protection at least as good as the provisions in ISO DIS 15031-7; dated October 1998 (SAE J2186 dated October 1996) provided that the security exchange is conducted using the protocols and diagnostic connector as prescribed in Section 6.5 of Annex XI, Appendix 1. Any removable calibration memory chips must be potted, encased in a sealed container or protected by electronic algorithms and must not be changeable without the use of specialised tools and procedures. 5.1.4.2. Computer-coded engine operating parameters must not be changeable without the use of specialized tools and procedures (e. g. soldered or potted computer components or sealed (or soldered) computer enclosures). 5.1.4.3. In the case of mechanical fuel-injection pumps fitted to compression-ignition engines, manufacturers must take adequate steps to protect the maximum fuel delivery setting from tampering while a vehicle is in service. 5.1.4.4. Manufacturers may apply to the approval authority for an exemption to one of these requirements for those vehicles which are unlikely to require protection. The criteria that the approval authority will evaluate in considering an exemption will include, but are not limited to, the current availability of performance chips, the high-performance capability of the vehicle and the projected sales volume of the vehicle. 5.1.4.5. Manufacturers using programmable computer code systems (e.g. electrical erasable programmable read-only memory, EEPROM) must deter unauthorised reprogramming. Manufacturers must include enhanced tamper-protection strategies and write protect features requiring electronic access to an off site computer maintained by the manufacturer. Methods giving an adequate level of tamper protection will be approved by the authority. 5.2.Application of tests Figure 1.5.2 illustrates the routes for type-approval of a vehicle. 5.2.1. Positive-ignition engined vehicles must be subject to the following tests: Type I (verifying the average tailpipe emissions after a cold start), Type II (carbon monoxide emission at idling speed), Type III (emission of crankcase gases), Type IV (evaporation emissions), Type V (durability of anti-pollution control devices), Type VI (verifying the average low ambient temperature carbon monoxide and hydrocarbon tailpipe emissions after a cold start, OBD-test. 5.2.2. Positive-ignition engined vehicles referred to in 8.1 must be subject to the following tests: type I (simulating the average tailpipe emissions after a cold start), type II (carbon monoxide emission at idling speed), type III (emissions of crankcase gases). 5.2.2. Positive-ignition engine powered vehicle fuelled with LPG or NG (mono or bi-fuel) shall be subjected to the following tests: Type I (verifying the average tailpipe emissions after a cold start), Type II (carbon monoxide emissions at idling speed), Type III (emission of crankcase gases), Type IV (evaporative emissions), where applicable, Type V (durability of pollution control devices), Type VI (verifying the average low ambient temperature carbon monoxide and hydrocarbon tailpipe emissions after a cold start), where applicable, OBD test, where applicable. 5.2.3. Compression-ignition engined vehicles must be subject to the following tests: Type I (verifying the average tailpipe emissions after a cold start) Type V (durability of anti-pollution control devices) and, where applicable, OBD test. 5.2.4. Compression-ignition engined vehicles referred to in 8.1 must be subject to the following test: type I (simulating the average tailpipe emissions after a cold start — gaseous polluants only.) 5.3.Description of tests 5.3.1. Type I test (simulating the average tailpipe emissions after a cold start). 5.3.1.1. Figure I.5.3 illustrates the routes for type I test. This test must be carried out on all vehicles referred to in section 1, of a maximum mass not exceeding 3,5 tonnes. 5.3.1.2. The vehicle is placed on a chassis dynamometer equipped with a means of load and inertia simulation. 5.3.1.2.1. A test lasting a total ofvehicles referred to in 8.1, a test lasting a total of 19 minutes and 40 seconds, made up of two parts, One and Two, is performed without interruption. An unsampled period of not more than 20 seconds may, with the agreement of the manufacturer, be introduced between the end of Part One and the beginning of Part Two in order to facilitate adjustment of the test equipment. 5.3.1.2.1.1. Vehicles that are fuelled with LPG or NG shall be tested in the type I test for variations in the composition of LPG or NG, as set out in Annex XII. Vehicles that can be fuelled either with petrol or with LPG or NG shall be tested in the type I test on both fuels, of which the fuelling on LPG or NG has to be performed for variation in the composition of LPG or NG, as set out in Annex XII. 5.3.1.2.1.2. Notwithstanding the requirement of point 5.3.1.2.1.1, 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 type I as vehicles that can only run on a gaseous fuel. 5.3.1.2.2. Part One of the test is made up of four elementary urban cycles. Each elementary urban cycle comprises fifteen phases (idling, acceleration, steady speed, deceleration, etc.). 5.3.1.2.3. Part Two of the test is made up of one extra urban cycle. The extra urban cycle comprises 13 phases (idling, acceleration, steady speed, deceleration, etc.).
Figure I.5.2 Different routes for type-approval and extensions The Commission will study further the question of extending the type-approval test to vehicles in categories M2 and N2 with a reference mass not exceeding 2840 kg and put forward proposals no later than 2004 in accordance with the procedure laid down in Article 13 of Directive 70/156/EEC, for measures to be applied in 2005.
Type-approval test Positive-ignition engined vehicles of categories M and N Compression-ignition engined vehicles of categories M1 and N1
Petrol-fuelled vehicle Bi-fuel vehicle Mono-fuel vehicle
Type I Yes (maximum mass ≤ 3,5 t) Yes (test with both fuel types) (maximum mass ≤ 3,5 t) Yes (maximum mass ≤ 3,5 t) Yes (maximum mass ≤ 3,5 t)
Type II Yes Yes (test with both fuel types) Yes
Type III Yes Yes (test only with petrol) Yes
Type IV Yes (maximum mass ≤ 3,5 t) Yes (test only with petrol) (maximum mass ≤ 3,5 t)
Type V Yes (maximum mass ≤ 3,5 t) Yes (test only with petrol) (maximum mass ≤ 3,5 t) Yes (maximum mass ≤ 3,5 t) Yes (maximum mass ≤ 3,5 t)
Type VI Yes (maximum mass ≤ 3,5 t) Yes (maximum mass ≤ 3,5 t) (test only with petrol)
Extension Section 6 Section 6 Section 6 Section 6; M2 and N2 with a reference mass ≤ 2840 kg
On-board diagnostics Yes, in accordance with section 8.1.1 or 8.4 Yes, in accordance with section 8.1.2 or 8.4 Yes, in accordance with section 8.1.2 or 8.4 Yes, in accordance with sections 8.2, 8.3 or 8.4
5.3.1.2.4. For the vehicles referred to in 8.1, a test comprising only four elementary urban cycles (Part One) is performed without interruption, lasting a total of 13 minutes. 5.3.1.2.5. During the test the exhaust gases are diluted and a proportional sample collected in one or more bags. The exhaust gases of the vehicle tested are diluted, sampled and analyzed, following the procedure described below, and the total volume of the diluted exhaust is measured. Not only the carbon monoxide, hydrocarbon and nitrogen oxide emissions, but also the particulate pollutant emissions from vehicles equipped with compression-ignition engines are recorded.
5.3.1.3. The test is carried out using the procedure described in Annex III. The methods used to collect and analyse the gases and to remove and weigh the particulates must be as prescribed. 5.3.1.4. Subject to the requirements of 5.3.1.5 the test must be repeated three times.The results are multiplied by the appropriate deterioration factors obtained from 5.3.5. The resulting masses of gaseous emissions and, in the case of vehicles equipped with compression-ignition engines, the mass of particulates obtained in each test must be less than the limits shown in the tables below:
For compression ignition engines. Except vehicles the maximum mass of which exceeds 2500 kg. And those Category M vehicles which are specified in note 2.
CategoryClass Reference mass(RW)(kg) Limit values
Mass of carbon monoxide(CO) Mass of hydrocarbons(HC) Mass of oxides of nitrogen(NOx) Combined mass of hydrocarbons and oxides of nitrogen(HC + NOx) Mass of particulates(PM)
L1(g/km) L2(g/km) L3(g/km) L2 + L3(g/km) L4(g/km)
Petrol Diesel Petrol Diesel Petrol Diesel Petrol Diesel Diesel
A (2000) M all 2,3 0,64 0,20 0,15 0,50 0,56 0,05
N1 I RW ≤ 1305 2,3 0,64 0,20 0,15 0,50 0,56 0,05
II 1305 < RW ≤ 1760 4,17 0,80 0,25 0,18 0,65 0,72 0,07
III 1760 < RW 5,22 0,95 0,29 0,21 0,78 0,86 0,10
B (2005) M all 1,0 0,50 0,10 0,08 0,25 0,30 0,025
N1 I RW ≤ 1305 1,0 0,50 0,10 0,08 0,25 0,30 0,025
II 1305 < RW ≤ 1760 1,81 0,63 0,13 0,10 0,33 0,39 0,04
III 1760 < RW 2,27 0,74 0,16 0,11 0,39 0,46 0,06
Until 30 September 1999, for vehicles fitted with diesel engines of the direct injection type, the limit values L2and L3are the following:
L2 L3
category M and N1 class I: 0,9 0,10
category N1 class II: 1,3 0,14
category N1 class III: 1,6 0,20
Except: vehicles designed to carry more than six occupants including the driver, vehicles whose maximum mass exceed 2500 kg. And those cagtegory M vehicles which are specified in footnote (2). Category/class of vehicle Limit values Category Class Reference massRW(kg) Mass of carbon monoxideL1(g/km) Combined mass of hydrocarbons and oxides of nitrogenL2(g/km) Mass of particulatesL3(g/km) Petrol Diesel Petrol Diesel Diesel M — all 2,2 1,0 0,5 0,7 0,08 N1 I RW ≤ 1250 2,2 1,0 0,5 0,7 0,08 II 1250 < RW ≤ 1700 4,0 1,25 0,6 1,0 0,12 III 1700 < RW 5,0 1,5 0,7 1,2 0,17 5.3.1.4.1. Notwithstanding the requirements of 5.3.1.4, for each pollutant or combination of pollutants, one of the three resulting masses obtained may exceed, by not more than 10 %, the limit prescribed, provided the arithmetical mean of the three results is below the prescribed limit. Where the prescribed limits are exceeded for more than one pollutant it is immaterial whether this occurs in the same test or in different testsWhen one of the three results corresponding to each pollutant or combination exceeds the limit value prescribed in 5.3.1.4 by more than 10 %, the test may, for the vehicle concerned, be continued as specified in 5.3.1.4.2.. 5.3.1.4.2. The number of tests prescribed in 5.3.1.4 may, at the request of the manufacturer, be increased to 10 provided that the arithmetical mean ( x-i ) of the first three results obtained for each pollutant or combined total of two pollutants subject to limitation falls between 100 and 110 % of the limit. In this case, the requirement is only that the arithmetical mean of all ten results obtained for each pollutant or combined total of two pollutants subject to limitation must be less than the limit value ( x- < L ). 5.3.1.4.2. When the tests are performed with gaseous fuels, the resulting mass of gaseous emissions shall be less than the limits for petrol-engined vehicles in the above table.
5.3.1.5. The number of tests prescribed in 5.3.1.4 is reduced in the conditions hereinafter defined, where V1 is the result of the first test and V2 the result of the second test for each pollutant or for the combined emission of two pollutants subject to limitation. 5.3.1.5.1. Only one test is performed if the result obtained for each pollutant or for the combined emission of two pollutants subject to limitation, is less than or equal to 0,70 L (ie. V1 ≤ 0,70 L). 5.3.1.5.2. If the requirement of 5.3.1.5.1 is not satisfied, only two tests are performed if, for each pollutant or for the combined emission of two pollutants subject to limitation, the following requirements are met:V1 ≤ 0,85 L and V1 + V2 ≤ 1,70 L and V2 ≤ L.
5.3.2.Type II test (carbon monoxide emission test at idling speed) 5.3.2.1. This test is carried out on vehicles powered by a positive-ignition engine to which the test specified in 5.3.1 does not apply. 5.3.2.1.1. Vehicles which can be fuelled either with petrol or with LPG or NG shall be tested in the test type II on both fuels. 5.3.2.1.2. Notwithstanding the requirement of point 5.3.2.1.1 above, 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 type II test as vehicles that can only run on a gaseous fuel. 5.3.2.2. When tested in accordance with Annex IV, the carbon monoxide content by volume of the exhaust gases emitted with the engine idling must not exceed 3,5 % at the setting specified by the manufacturer and must not exceed 4,5 % within the range of adjustments specified in that Annex. 5.3.3.Type III test (verifying emissions of crankcase gases) 5.3.3.1. This test must be carried out on all vehicles referred to in section 1 except those having compression-ignition engines. 5.3.3.1.1. Vehicles that can be fuelled either with petrol or with LPG or NG should be tested in the type III test on petrol only. 5.3.3.1.2. Notwithstanding the requirement of point 5.3.3.1.1, 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 type III test as vehicles that can only run on a gaseous fuel. 01970L0220-20070101_en_img_1 5.3.3.2. When tested in accordance with Annex V, the engine's crankcase ventilation system must not permit the emission of any of the crankcase gases into the atmosphere. 5.3.4.Type IV test (determination of evaporative emissions) 5.3.4.1. This test must be carried out on all vehicles referred to in Section 1 except those vehicles having a compression-ignition engine, and the vehicles fuelled with LPG or NG. 5.3.4.1.1. Vehicles that can be fuelled either with petrol or with LPG or NG should be tested in the type IV test on petrol only. 5.3.4.2. When tested in accordance with Annex VI, evaporative emissions shall be less than 2 g/test. 5.3.5.This section is applicable to new types from 1 January 2002.Type VI test (verifying the average low ambient temperature carbon monoxide and hydrocarbon tailpipe emissions after a cold start) 5.3.5.1. This test must be carried out on all vehicles of category M1 and N1 equipped with a positive-ignition engine except such vehicles that run only on a gaseous fuel (LPG or NG). 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 Type VI test as vehicles that can only run on a gaseous fuel.Vehicles which can be fuelled with petrol and either LPG or NG shall be tested in the test Type VI on petrol only.This section is applicable to new types of vehicles of category M1 and category N1, class I, except vehicles designed to carry more than six occupants and vehicles the maximum mass of which exceeds 2500 kgThis section is applicable to new types from 1 January 2002..From 1 January 2003, this section is applicable to new types of vehicles of category N1 classes II and III, new types of category M1 vehicles designed to carry more than six occupants and new types of vehicles of category M1 with a maximum mass greater than 2500 kg but not exceeding 3500 kg. 5.3.5.1.1. The vehicle is placed on a chassis dynamometer equipped with a means of load an inertia simulation. 5.3.5.1.2. The test consists of the four elementary urban driving cycles of part one of the Type I test. The Part One test is described in Annex III, Appendix 1 and illustrated in figures III.1.1 and III.1.2 of the Appendix. The low ambient temperature test lasting a total of 780 seconds must be carried out without interruption and start at engine cranking. 5.3.5.1.3. The low ambient temperature test must be carried out at an ambient test temperature of 266 °K (-7 °C). Before the test is carried out the test vehicles must be conditioned in a uniform manner to ensure that the test results may be reproducible. The conditioning and other test procedures are carried out as described in Annex VII. 5.3.5.1.4. During the test the exhaust gases are diluted and a proportional sample collected. The exhaust gases of the vehicle tested are diluted, sampled and analysed, following the procedure described in Annex VII, and the total volume of the diluted exhaust is measured. The diluted exhaust gases are analysed for carbon monoxide and hydrocarbons. 5.3.5.2. Subject to the requirements in 5.3.5.2.2 and 5.3.5.3 the test must be performed three times. The resulting mass of carbon monoxide and hydrocarbon emission must be less than the limits shown in the table below:
Except vehicles designed to carry more than six occupants and vehicles the maximum mass of which exceeds 2500 kg. And those category M1 vehicles which are specified in note 1.
Test temperature 266 K (– 7 °C)
Category Class Mass of carbon monoxide (CO)L1 (g/km) Mass of hydrocarbons (HC)L2 (g/km)
M1 15 1,8
N1 I 15 1,8
N1 II 24 2,7
III 30 3,2
5.3.5.2.1. Notwithstanding the requirements of 5.3.5.2, for each pollutant, not more than one of the three results obtained may exceed the limit prescribed by not more than 10 %, provided the arithmetical mean value of the three results is below the prescribed limit. Where the prescribed limits are exceeded for more than one pollutant it is immaterial whether this occurs in the same test or in different tests. 5.3.5.2.2. The number of tests prescribed in 5.3.5.2 may, at the request of the manufacturer, be increased to 10 provided that the arithmetical mean of the first three results falls between 100 % to 110 % of the limit. In this case, the requirement after testing is only that the arithmetical mean of all 10 results must be less than the limit value. 5.3.5.3. The number of tests prescribed in 5.3.5.2 may be reduced according to 5.3.5.3.1 and 5.3.5.3.2. 5.3.5.3.1. Only one test is performed if the result obtained for each pollutant of the first test is less than or equal to 0,70 L. 5.3.5.3.2. If the requirement of 5.3.5.3.1 is not satisfied, only two tests are performed if for each pollutant the result of the first test is less than or equal to 0,85 L and the sum of the first two results is less than or equal to 1,70 L and the result of the second test is less than or equal to L.(V1 ≤ 0,85 L and V1 + V2 ≤ 1,70 L and V2 ≤ L). 5.3.6.Type V test (durability of anti-pollution devices) 5.3.6.1. This test must be carried out on all vehicles referred to in Section 1 to which the test specified in 5.3.1 applies. The test represents an ageing test of 80000 kilometres driven in accordance with the programme described in Annex VII on a test track, on the road or on a chassis dynamometer. 5.3.6.1.1. Vehicles that can be fuelled either with petrol or with LPG or NG should be tested in the type V test on petrol only. 5.3.6.2. Notwithstanding the requirement of 5.3.6.1 a manufacturer may choose to have the deterioration factors from the following table used as an alternative to testing to 5.3.6.1.1.
For compression-ignition engined vehicles.
Engine Category Deterioration factors
CO HC NOx HC + NOx Particulates
Positive-ignition engines 1,2 1,2 1,2
Compression-ignition engines 1,1 1,0 1,0 1,2
At the request of the manufacturer, the technical service may carry out the type I test before the type V test has been completed using the deterioration factors in the table above. On completion of the type V test, the technical service may then amend the type-approval results recorded in Annex IX by replacing the deterioration factors in the above table with those measured in the type V test.
5.3.6.3. Deterioration factors are determined using either the procedure in 5.3.6.1 or using the values in the table in 5.3.6.2. The deterioration factors are used to establish compliance with the requirements of 5.3.1.4.
5.3.7.Emissions data required for roadworthiness testing 5.3.7.1. This requirement applies to all vehicles powered by a positive-ignition engine for which EC type-approval is sought in accordance with this Directive. 5.3.7.2. When tested in accordance with Annex IV (type II test) at normal idling speed: the carbon monoxide content by volume of the exhaust gases emitted must be recorded, the engine speed during the test must be recorded, including any tolerances. 5.3.7.3. When tested at "high idle" speed (i. e. > 2000 min-1): the carbon monoxide content by volume of the exhaust gases emitted must be recorded, the Lambda valueThe Lambda value must be calculated using the simplified Brettschneider equation as follows: 01970L0220-20070101_en_img_2Where: [ ]Concentration in % vol. K1Conversion factor for NDIR measurement to FID measurement (provided by manufacturer of measurement equipment) HcvAtomic ratio of hydrogen to carbon [1,73], in the case of LPG [2,53], in the case of NG [4,0] OcvAtomic ratio of oxygen to carbon [0,02], in the case of LPG [zero], in the case of NG [zero]. must be recorded. the engine speed during the test must be recorded, including any tolerances. 5.3.7.4. The engine oil temperature at the time of the test must be measured and recorded. 5.3.7.5. The table in section 1.9 of the Appendix to Annex X must be completed. 5.3.7.6. The manufacturer must confirm the accuracy of the Lambda value recorded at the time of type-approval in section 5.3.7.3 as being representative of typical production vehicles within 24 months of the date of the granting of type-approval by the technical service. An assessment must be made on the basis of surveys and studies of production vehicles. 5.3.8.Replacement catalytic converters and original replacement catalytic converters 5.3.8.1. Replacement catalytic converters intended to be fitted to EC type-approved vehicles must be tested in accordance with Annex XIII. 5.3.8.2. Original replacement catalytic converters, which are of a type covered by point 1.10 of the Appendix to Annex X and are intended for fitment to a vehicle to which the relevant type-approval document refers, do not need to comply with Annex XIII to this Directive provided they fulfil the requirements of sections 5.3.8.2.1 and 5.3.8.2.2. 5.3.8.2.1. MarkingOriginal replacement catalytic converters shall bear at least the following identifications: 5.3.8.2.1.1.the vehicle manufacturer's name or trade mark; 5.3.8.2.1.2. the make and identifying part number of the original replacement catalytic converter as recorded in the information mentioned in point 5.3.8.3. 5.3.8.2.2. DocumentationOriginal replacement catalytic converters shall be accompanied by the following information: 5.3.8.2.2.1. the vehicle manufacturer's name or trade mark; 5.3.8.2.2.2. make and identifying part number of the original replacement catalytic converter as recorded in the information mentioned in point 5.3.8.3; 5.3.8.2.2.3. the vehicles for which the original replacement catalytic converter is of a type covered by point 1.10 of the Appendix to Annex X, including, where applicable, a marking to identify if the original replacement catalytic converter is suitable for fitting to a vehicle that is equipped with an on-board diagnostic (OBD) system; 5.3.8.2.2.4. installation instructions, where necessary; 5.3.8.2.2.5. this information shall be provided either: as a leaflet accompanying the original replacement catalytic converter, or on the packaging in which the original replacement catalytic converter is sold, or or by any other applicable means. In any case, the information must be available in the product catalogue distributed to points of sale by the vehicle manufacturer. 5.3.8.3. The vehicle manufacturer shall provide to the technical service and/or approval authority the necessary information in electronic format which makes the link between the relevant part numbers and the type approval documentation.This information shall contain: make(s) and type(s) of vehicle, make(s) and type(s) of original replacement catalytic converter, part number(s) of original replacement catalytic converter, type-approval number of the relevant vehicle type(s).
6.MODIFICATIONS OF THE TYPE AND AMENDMENTS TO APPROVALS In the case of modifications of the type approved pursuant to this Directive, the provisions of Article 5 of Directive 70/156/EEC and, if applicable, the following special provisions shall apply: 6.1.Tailpipe emission related extension (type I, type II and type VI tests) 6.1.1.Vehicle types of different reference masses 6.1.1.1. Approval granted to a vehicle type may be extended only to vehicle types of a reference mass requiring the use of the next two higher equivalent inertia or any lower equivalent inertia. 6.1.1.2. In the case of vehicles of category N1 and vehicles of category M referred to in note 2 of Section 5.3.1.4, if the reference mass of the vehicle type for which extension of the approval is requested requires the use of a flywheel of equivalent inertia lower than that used for the vehicle type already approved, extension of the approval is granted if the masses of the pollutants obtained from the vehicle already approved are within the limits prescribed for the vehicle for which extension of the approval is requested 6.1.2.Vehicle types with different overall gear ratios Approval granted to a vehicle type may under the following conditions be extended to vehicle types which differ from the type approved only in respect of their transmission ratios: 6.1.2.1. Fore each of the transmission rations used in the type I and type VI tests, it is necessary to determine the proportion, E = V2 - V1V1 where, at an engine speed of 1000 rpm, V1 is the speed of the vehicle-type approved and V2 is the speed of the vehicle type for which extension of the approval is requested. 6.1.2.2. If, for each gear ratio, E ≤ 8 %, the extension is granted without repeating the type I and type VI tests. 6.1.2.3. If, for at least one gear ratio, E ≤ 8 %, and if, for each gear ratio, E ≤ 13 %, the type I and type VI tests must be repeated, but may be performed in a laboratory chosen by the manufacturer subject to the approval of the technical service. The report of the tests must be sent to the technical service responsible for the type-approval tests. 6.1.3.Vehicle types of different reference masses and different overall transmission ratios Approval granted to a vehicle type may be extended to vehicle types differing from the approved type only in respect of their reference mass and their overall transmission ratios, provided that all the conditions prescribed in 6.1.1 and 6.1.2 are fulfilled. 6.1.4.Note: When a vehicle type has been approved in accordance with 6.1.1 to 6.1.3, such approval may not be extended to other vehicle types. 6.2.Evaporative emissions (type IV test) 6.2.1. Approval granted to a vehicle type equipped with a control system for evaporative emissions may be extended under the following conditions: 6.2.1.1. The basic principle of fuel/air metering (e.g. single point injection, carburettor) must be the same. 6.2.1.2. The shape of the fuel tank and the material of the fuel tank and liquid fuel hoses must be identical. The worst-case family with regard to the cross-section and approximate hose length must be tested. Whether non-identical vapour/liquid separators are acceptable is decided by the technical service responsible for the type-approval tests. The fuel tank volume must be within a range of ± 10 %. The setting of the tank relief valve must be identical. 6.2.1.3. The method of storage of the fuel vapour must be identical, i.e. trap form and volume, storage medium, air cleaner (if used for evaporative emission control), etc. 6.2.1.4. The carburettor bowl fuel volume must be within a 10 millilitre range. 6.2.1.5. The method of purging of the stored vapour must be identical (e.g. air flow, start point or purge volume over driving cycle). 6.2.1.6. The method of sealing and venting of the fuel metering system must be identical. 6.2.2. Further notes: (i)different engine sizes are allowed; (ii)different engine powers are allowed; (iii)automatic and manual gearboxes, two and four wheel transmissions are allowed; (iv)different body styles are allowed; (v)different wheel and tyre sizes are allowed. 6.3.Durability of anti-pollution devices (type V test) 6.3.1. Approval granted to a vehicle type may be extended to different vehicle types, provided that the engine/pollution control system combination is identical to that of the vehicle already approved. To this end, those vehicle types whose parameters described below are identical or remain within the limit values prescribed are considered to belong to the same engine/pollution control system combination. 6.3.1.1. Engine: number of cylinders, engine capacity (± 15 %), configuration of the cylinder block, number of valves, fuel system, type of cooling system, combustion process, cylinder bore centre to centre dimensions. 6.3.1.2. Pollution control system: Catalytic converters: number of catalytic converters and elements, size and shape of catalytic converters (volume of monolith ± 10 %), type of catalytic activity (oxidizing, three-way, …), precious metal load (identical or higher), precious metal ratio (± 15 %), substrate (structure and material), cell density, type of casing for the catalytic converter(s), location of catalytic converters (position and dimension in the exhaust system, that does not produce a temperature variation of more than 50 K at the inlet of the catalytic converter).This temperature variation shall be checked under stabilized conditions at a speed of 120 km/h and the load setting of type I test. Air injection: with or without type (pulsair, air pumps, …). EGR: with or without. 6.3.1.3. Inertia category: the two inertia categories immediately above and any inertia category below. 6.3.1.4. The durability test may be achieved by using a vehicle, the body style, gear box (automatic or manual) and size of the wheels or tyres of which are different from those of the vehicle type for which the type approval is sought. 6.4.On-board diagnostics 6.4.1. Approval granted to a vehicle type with respect to the OBD system may be extended to different vehicle types belonging to the same vehicle-OBD family as described in Annex XI, Appendix 2. The engine emission control system must be identical to that of the vehicle already approved and comply with the description of the OBD engine family given in Annex XI, Appendix 2, regardless of the following vehicle characteristics: engine accessories, tyres, equivalent inertia, cooling system, overall gear ratio, transmission type, type of bodywork. 7.CONFORMITY OF PRODUCTION 7.1. Measures to ensure the conformity of production must be taken in accordance with the provisions of Article 10 of Directive 70/156/EEC, as last amended by Directive 96/27/EEC (whole vehicle type-approval). That Article entrusts the manufacturer with the responsibility for taking measures to ensure the conformity of production to the type approved. Conformity of production is checked on the basis of the description in the type-approval certificate set out in Annex X to this Directive.As a general rule, conformity of production with regard to limitation of tailpipe and evaporative emissions from the vehicle is checked on the basis of the description in the type-approval certificate set out in Annex X and, where necessary, of all or some of the tests of types I, II, III and IV described in section 5.2. Conformity of in-service vehicles With reference to type-approvals granted for emissions, these measures must also be appropriate for confirming the functionality of the emission control devices during the normal useful life of the vehicles under normal conditions of use (conformity of in-service vehicles properly maintained and used). For the purpose of this Directive these measures must be checked for a period of up to 5 years of age or 80000 km, whichever is the sooner, and from 1 January 2005, for a period of up to five years of age or 100000 km, whichever is the sooner. 7.1.1. Audit of in-service conformity by the type-approval authority is conducted on the basis of any relevant information that the manufacturer has, under procedures similar to those defined in Article 10(1) and (2) of Directive 70/156/EEC and in points 1 and 2 of Annex X to that Directive.Figures I.8 and I.9 in Appendix 4 to this Annex illustrate the procedure for in-service conformity checking. 7.1.1.1. Parameters defining the in-service familyThe in-service family may be defined by basic design parameters which must be common to vehicles within the family. Accordingly, those vehicle types which have in common, or within the stated tolerances, at least the parameters described below, can be considered as belonging to the same in-service family: combustion process (2-stroke, 4-stroke, rotary), number of cylinders, configuration of the cylinder block (in-line, V, radial, horizontally opposed, other). The inclination or orientation of the cylinders is not a criteria), method of engine fuelling (e.g. indirect or direct injection), type of cooling system (air, water, oil), method of aspiration (naturally aspirated, pressure charged), fuel for which the engine is designed (petrol, diesel, NG, LPG, etc). Bi-fuelled vehicles may be grouped with dedicated fuel vehicles providing one of the fuels is common, type of catalytic converter (three-way catalyst or other(s)), type of particulate trap (with or without), exhaust gas recirculation (with or without), engine cylinder capacity of the largest engine within the family minus 30 %. 7.1.1.2. An audit of in-service conformity will be conducted by the type-approval authority on the basis of information supplied by the manufacturer. Such information must include, but is not limited to, the following: 7.1.1.2.1. the name and address of the manufacturer; 7.1.1.2.2. the name, address, telephone and fax numbers and e-mail address of his authorised representative within the areas covered by the manufacturer's information; 7.1.1.2.3. the model name(s) of the vehicles included in the manufacturer's information; 7.1.1.2.4. where appropriate, the list of vehicle types covered within the manufacturer's information, i.e. the in-service family group in accordance with section 7.1.1.1; 7.1.1.2.5. the vehicle identification number (VIN) codes applicable to these vehicle types within the in-service family (VIN prefix); 7.1.1.2.6. the numbers of the type approvals applicable to these vehicle types within the in-service family, including, where applicable, the numbers of all extensions and field fixes/recalls (re-works); 7.1.1.2.7. details of extensions, field fixes/recalls to those type approvals for the vehicles covered within the manufacturer's information (if requested by the type-approval authority); 7.1.1.2.8. the period of time over which the manufacturer's information was collected; 7.1.1.2.9. the vehicle build period covered within the manufacturer's information (e.g. vehicles manufactured during the 2001 calendar year); 7.1.1.2.10. the manufacturer's in-service conformity checking procedure, including: 7.1.1.2.10.1.vehicle location method; 7.1.1.2.10.2.vehicle selection and rejection criteria; 7.1.1.2.10.3.test types and procedures used for the programme; 7.1.1.2.10.4.the manufacturer's acceptance/rejection criteria for the in-service family group; 7.1.1.2.10.5.geographical area(s) within which the manufacturer has collected information; 7.1.1.2.10.6.sample size and sampling plan used; 7.1.1.2.11. the results from the manufacturer's in-service conformity procedure, including: 7.1.1.2.11.1.identification of the vehicles included in the programme (whether tested or not). The identification will include: model name, vehicle identification number (VIN), vehicle registration number, date of manufacture, region of use (where known), tyres fitted; 7.1.1.2.11.2.the reason(s) for rejecting a vehicle from the sample; 7.1.1.2.11.3.service history for each vehicle in the sample (including any re-works); 7.1.1.2.11.4.repair history for each vehicle in the sample (where known); 7.1.1.2.11.5.test data, including: date of test, location of test, distance indicated on vehicle odometer, test fuel specifications (e.g. test reference fuel or market fuel), test conditions (temperature, humidity, dynamometer inertia weight), dynamometer settings (e.g. power setting), test results (from at least three different vehicles per family); 7.1.1.2.12. records of indication from the OBD system. 7.1.2. The information gathered by the manufacturer must be sufficiently comprehensive to ensure that in-service performance can be assessed for normal conditions of use as defined in section 7.1 and in a way representative of the manufacturer's geographic penetration.For the purpose of this Directive, the manufacturer shall not be obliged to carry out an audit of in-service conformity for a vehicle type if he can demonstrate to the satisfaction of the type-approval authority that the annual sales of that vehicle type are less than 5000 per annum in the Community. 7.1.3. If a type I test is to be carried out and a vehicle type-approval has one or several extensions, the tests will be carried out either on the vehicle described in the initial information package or on the vehicle described in the information package relating to the relevant extension. 7.1.3.1.Checking the conformity of the vehicle for a type I test. After selection by the authority, the manufacturer must not undertake any adjustment to the vehicles selected. 7.1.3.1.1. Three vehicles are selected at random in the series and are tested as described in Section 5.3.1 of this Annex. The deterioration factors are used in the same way. The limit values are given in Section 5.3.1.4 of this Annex. 7.1.3.1.2. If the authority is satisfied with the production standard deviation given by the manufacturer in accordance with Annex X to Directive 70/156/EEC, the tests are carried out according to Appendix 1 of this Annex.If the authority is not satisfied with the production standard deviation given by the manufacturer in accordance with Annex X to Directive 70/156/EEC, the tests are carried out according to Appendix 2 of this Annex. 7.1.3.1.3. The production of a series is deemed to conform or not to conform on the basis of a sampling test of the vehicles once a pass decision is reached for all the pollutants or a fail decision is reached for one pollutant, according to the test criteria applied in the appropriate appendix.When a pass decision has been reached for one pollutant, that decision will not be changed by any additional tests carried out to reach a decision for the other pollutants.If no pass decision is reached for all the pollutants and no fail decision is reached for one pollutant, a test is carried out on another vehicle (see Figure I/7). 7.1.3.2. Notwithstanding the requirements of Section 3.1.1 of Annex III, the tests will be carried out on vehicles coming straight off the production line. 7.1.3.2.1. However, at the request of the manufacturer, the tests may be carried out on vehicles which have completed: a maximum of 3000 km for vehicles equipped with a positive ignition engine, a maximum of 15000 km for vehicles equipped with a compression ignition engine, In both these cases, the running-in procedure will be conducted by the manufacturer, who must undertake not to make any adjustments to these vehicles. 01970L0220-20070101_en_img_3 7.1.3.2.2. If the manufacturer wishes to run in the vehicles, ("x" km, where x ≤ 3000 km for vehicles equipped with a positive ignition engine and x ≤ 15000 km for vehicles equipped with a compression ignition engine), the procedure will be as follows: the pollutant emissions (type I) will be measured at zero and at "x" km on the first tested vehicle, the evolution coefficient of the emissions between zero and "x" km will be calculated for each of the pollutants: 01970L0220-20070101_en_img_4This may be less than 1, the other vehicles will not be run in, but their zero km emissions will be multiplied by the evolution coefficient.In this case, the values to be taken will be: the values at "x" km for the first vehicle, the values at zero km multiplied by the evolution coefficient for the other vehicles. 7.1.3.2.3. All these tests may be conducted with commercial fuel. However, at the manufacturer's request, the reference fuels described in Annex VIII may be used. 7.1.4. If a type III test is to be carried out, it must be conducted on all vehicles selected for the type I COP test (7.1.1.1.1). The conditions laid down in 5.3.3.2 must be complied with. 7.1.5. If a type IV test is to be carried out, it must be conducted in accordance with Section 7 of Annex VI. On-board Diagnostics (OBD) 7.1.6. If a verification of the performance of the OBD system is to be carried out, it must be conducted in accordance with the following: 7.1.6.1. When the approval authority determines that the quality of production seems unsatisfactory a vehicle is randomly taken from the series and subjected to the tests described in Annex XI, Appendix 1. 7.1.6.2. The production is deemed to conform if this vehicle meets the requirements of the tests described in Annex XI, Appendix 1. 7.1.6.3. If the vehicle taken from the series does not satisfy the requirements of section 7.1.6.1 a further random sample of four vehicles must be taken from the series and subjected to the tests described in Annex XI, Appendix 1. The tests may be carried out on vehicles which have been run in for no more than 15000 km. 7.1.6.4. The production is deemed to conform if at least 3 vehicles meet the requirements of the tests described in Annex XI, Appendix 1. 7.1.7. On the basis of the audit referred to in section 7.1.1, the type-approval authority must either: decide that the in-service conformity of a vehicle type or a vehicle in-service family is satisfactory and not take any further action, decide that the data provided by the manufacturer is insufficient to reach a decision and request additional information or test data from the manufacturer, or decide that the in-service conformity of a vehicle type, or vehicle type(s) that is/are part of an in-service family, is unsatisfactory and proceed to have such vehicle type(s) tested in accordance with Appendix 3 to this Annex. In the case that the manufacturer has been permitted to not carry out an audit for a particular vehicle type in accordance with section 7.1.2, the type-approval authority may proceed to have such vehicle types tested in accordance with Appendix 3 to this Annex. 7.1.7.1. Where type I tests are considered necessary to check the conformity of emission control devices with the requirements for their performance while in service, such tests must be carried out using a test procedure meeting the statistical criteria defined in Appendix 4 to this Annex. 7.1.7.2. The type-approval authority, in cooperation with the manufacturer, must select a sample of vehicles with sufficient mileage whose use under normal conditions can be reasonably assured. The manufacturer must be consulted on the choice of the vehicles in the sample and be allowed to attend the confirmatory checks of the vehicles. 7.1.7.3. The manufacturer is authorized, under the supervision of the type-approval authority, to carry out checks, even of a destructive nature, on those vehicles with emission levels in excess of the limit values with a view to establishing possible causes of deterioration which cannot be attributed to the manufacturer himself (e. g. use of leaded petrol before the test date). Where the results of the checks confirm such causes, those test results are excluded from the conformity check. 7.1.7.4. Where the type-approval authority is not satisfied with the results of the tests in accordance with the criteria defined in Appendix 4, the remedial measures referred to in Article 11 (2) and in Annex X to Directive 70/156/EEC are extended to vehicles in service belonging to the same vehicle type which are likely to be affected with the same defects in accordance with section 6 of Appendix 3.The plan of remedial measures presented by the manufacturer must be approved by the type-approval authority. The manufacturer is responsible for the execution of the remedial plan as approved.The type-approval authority must notify its decision to all Member States within 30 days. The Member States may require the same plan of remedial measures be applied to all vehicles of the same type registered in their territory. 7.1.7.5. If a Member State has established that a vehicle type does not conform to the applicable requirements of Appendix 3 to this Annex, it must notify without delay the Member State which granted the original type-approval in accordance with the requirements of Article 11 (3) of Directive 70/156/EEC.Then, subject to the provision of Article 11(6) of Directive 70/156/EEC, the competent authority of the Member State which granted the original type-approval shall inform the manufacturer that a vehicle type fails to satisfy the requirements of these provisions and that certain measures are expected of the manufacturer. The manufacturer shall submit to the authority, within two months after this notification, a plan of measures to overcome the defects, the substance of which should correspond to the requirements of sections 6.1 to 6.8 of Appendix 3. The competent authority which granted the original type-approval shall, within two months, consult the manufacturer in order to secure agreement on a plan of measures and on carrying out the plan. If the competent authority which granted the original type-approval establishes that no agreement can be reached, the procedure pursuant to Article 11(3) and (4) of Directive 70/156/EEC shall be initiated. 8.TRANSITIONAL PROVISIONS 8.1. For the type-approval and verification of conformity of: vehicles other than those of category M1; passenger vehicles of category M1 designed to carry more than six occupants including the driver or whose maximum mass exceeds 2500 kilograms; off-road vehicles as defined in Annex I to Directive 70/156/EEC as last amended by Directive 87/403/EECOJ No L 220, 8. 8. 1987, p. 44., the test must be the Part One test. The limit values shown in the tables in 5.3.1.4 (type-approval) and 7.1.1.1 (conformity check) are replaced by the following: For vehicle type-approval:
Reference massRW(kg) Carbon monoxideL1(g/test) Combined emission of hydrocarbons and oxides of nitrogenL2(g/test)
RW ≤ 1020 58 19,0
1020 < RW ≤ 1250 67 20,5
1250 < RW ≤ 1470 76 22,0
1470 < RW ≤ 1700 84 23,5
1700 < RW ≤ 1930 93 25,0
1930 < RW ≤ 2150 101 26,5
2150 < RW 110 28,0
For conformity of production checks:
Reference massRW(kg) Carbon monoxideL1(g/test) Combined emission of hydrocarbons and oxides of nitrogenL2(g/test)
RW ≤ 1020 70 23,8
1020 < RW ≤ 1250 80 25,6
1250 < RW ≤ 1470 91 27,5
1470 < RW ≤ 1700 101 29,4
1700 < RW ≤ 1930 112 31,3
1930 < RW ≤ 2150 121 33,1
2150 < RW 132 35,0
8.2. The following provisions remain applicable until 31 December 1994 for vehicles newly put into service and type-approved before 1 July 1993: the transitional provisions laid down in section 8.3 (with the exception of 8.3.1.3) of Annex I to Directive 70/220/EEC, as amended by Directive 88/436/EEC, the provisions laid down for category M1See note (2) of Section 5.3.1.4. vehicles fitted with positive-ignition engines of a capacity of more than 2 litres, in Annex I to Directive 70/220/EEC as amended by Directive 88/76/EEC, the provisions laid down for vehicles with an engine capacity of less than 1,4 litres in Directive 70/220/EEC, as amended by Directive 89/458/EEC. At the manufacturer's request, the tests carried out in accordance with these requirements may be type-approved instead of undergoing the test referred to in sections 5.3.1, 5.3.5 and 7.1.1 of Annex I to Directive 70/220/EEC, as amended by Directive 91/441/EEC. 8.3. For vehicles of category M1See note (2) of Section 5.3.1.4. up to 1 July 1994 for type-approval and up to 31 December 1994 for the initial entry into service, andfor vehicles of category N1See note (3) of Section 5.3.1.4. up to 1 October 1994 for type-approval and up to 1 October 1995 for the initial entry into service,the limit values for the combined mass of hydrocarbons and nitrogen oxides and for the mass of particulates of vehicles fitted with compression ignition engines of the direct-injection type are those obtained by multiplying the values L2 and L3 in the tables in 5.3.1.4 (type-approval) and 7.1.1.1 (conformity check) by a factor of 1,4.
8.ON-BOARD DIAGNOSTIC (OBD) SYSTEM FOR MOTOR VEHICLES 8.1.Vehicles with positive-ignition engines 8.1.1.Petrol fuelled engines With effect from 1 January 2000 for new types and from 1 January 2001 for all types, vehicles of category M1 — except vehicles the maximum mass of which exceeds 2500 kg — and vehicles of category N1 class I, must be fitted with an OBD system for emission control in accordance with Annex XI.With effect from 1 January 2001 for new types and from 1 January 2002 for all types, vehicles of category N1 classes II and III and vehicles of category M1, the maximum mass of which exceeds 2500 kg, must be fitted with an OBD system for emission control in accordance with Annex XI. 8.1.2.LPG and natural gas fuelled vehicles With effect from 1 January 2003 for new types and from 1 January 2004 for all types, vehicles of category M1 — except vehicles the maximum mass of which exceeds 2500 kg — and vehicles of category N1 class I, running permanently or part-time on either LPG or natural gas fuel, must be fitted with an OBD system for emission control in accordance with Annex XI.With effect from 1 January 2006 for new types and from 1 January 2007 for all types, vehicles of category N1 classes II and III and vehicles of category M1, the maximum mass of which exceeds 2500 kg, running permanently or part-time on either LPG or natural gas fuel, must be fitted with an OBD system for emission control in accordance with Annex XI. 8.2.Vehicles with compression-ignition engines Vehicles of category M1, except vehicles designed to carry more than six occupants including the driver, vehicles whose maximum mass exceeds 2500 kg, from 1 January 2003 for new types and from 1 January 2004 for all types, must be fitted with an on-board diagnostic (OBD) system for emission control in accordance with Annex XI.Where new types of compression-ignition engined vehicles entering into service prior to this date are fitted with an OBD system, the provisions of sections 6.5.3 to 6.5.3.6 of Annex XI, Appendix 1, are applicable. 8.3.Vehicles with compression-ignition engines exempt from Section 8.2 From 1 January 2005 for new types and from 1 January 2006 for all types, vehicles of category M1 exempted by Section 8.2, except vehicles of category M1 equipped with compression-ignition engines and the maximum mass of which exceeds 2500 kg, and vehicles in category N1 class 1 equipped with compression-ignition engines, must be fitted with on-board diagnostic (OBD) systems for emission control in accordance with Annex XI.From 1 January 2006 for new types and 1 January 2007 for all types, vehicles in category N1, classes II and III equipped with compression-ignition engines and vehicles of category M1 equipped with compression-ignition engines and the maximum mass of which exceeds 2500 kg, must be fitted with on-board diagnostic (OBD) systems for emission control in accordance with Annex XI.Where compression-ignition engined vehicles entering into service prior to the dates given in this section are fitted with OBD systems, the provisions of Sections 6.5.3 to 6.5.3.6 of Annex XI, Appendix 1, are applicable. 8.4.Vehicles of other categories Vehicles of other categories or vehicles of category M1 and N1 not covered by 8.1, 8.2 or 8.3, may be fitted with an OBD system. In this case, Sections 6.5.3 to 6.5.3.6 of Annex XI, Appendix 1 are applicable.
ANNEX II INFORMATION DOCUMENT No …pursuant to Annex I of Directive 70/156/EECThe item numbers and footnotes used in this information document correspond to those set out in Annex I to Directive 70/156/EEC. Items not relevant for the purpose of this Directive are omitted. relating to EEC type-approval of a vehicle with respect to the measures to be taken against air pollution by emissions from motor vehicles (Directive 70/220/EEC, as last amended by Directive …/…/EC)The following information, if applicable, must be supplied in triplicate and incude a list of contents. Any drawings must be supplied in appropriate scale and in sufficient detail on size A4 or on a folder of A4 format. Photographs, if any, must show sufficient detail.If the systems, components or separate technical units have electronic controls, information concerning their performance must be supplied.01970L0220-20070101_en_img_501970L0220-20070101_en_img_601970L0220-20070101_en_img_701970L0220-20070101_en_img_801970L0220-20070101_en_img_901970L0220-20070101_en_img_1001970L0220-20070101_en_img_1101970L0220-20070101_en_img_12 ANNEX III TYPE I TEST(Verifying the average emission of tailpipe emissions after a cold start) 1.INTRODUCTION This Annex describes the procedure for the type I test defined in 5.3.1 of Annex I. When the reference fuel to be used is LPG or NG, the provisions of Annex XII shall apply additionally. 2.OPERATING CYCLE ON THE CHASSIS DYNAMOMETER 2.1.Description of the cycle The operating cycle on the chassis dynanometer is described in Appendix 1 to this Annex. 2.2.General conditions under which the cycle is carried out Preliminary testing cycles must be carried out if necessary to determine how best to actuate the accelerator and brake controls so as to achieve a cycle approximating to the theoretical cycle within the prescribed limits. 2.3.Use of gearbox 2.3.1. If the maximum speed which can be attained in first gear is below 15 km/h, the second, third and fourth gears are used for the elementary urban cycles (Part One) and the second, third, fourth and fifth gears for the extra-urban cycle (Part Two). The second, third and fourth gears may also be used for the urban cycle (Part One) and the second, third, four and fifth gears for the extra-urban cycle (Part Two) when the driving instructions recommend starting in second gear on level ground, or when first gear is therein defined as a gear reserved for cross-country driving, crawling or towing. For vehicles of category MSee note 2 of Section 5.3.1.4 of Annex I. with a maximum engine power of no more than 30 kw and a maximum speed not exceeding 130 km/h, the maximum speed of the extra-urban cycle (Part Two) is limited to 90 km/h until 1 July 1994.For vehicles of category N1See note 3 of Section 5.3.1.4 of Annex I. with a power-to-weight ratio of no more than 30 kw/tTechnically permissible laden mass as stated by the manufacturer. and a maximum speed not exceeding 130 km/h, the maximum speed of the extra-urban cycle (Part Two) is limited to 90 km/h until 1 January 1996 for vehicles of category I and until 1 January 1997 for vehicles of categories II and III. Vehicles which do not attain the acceleration and maximum speed values required in the operating cycle must be operated with the accelerator control fully depressed until they once again reach the required operating curve. Deviations from the operating cycle must be recorded in the test report. 2.3.2. Vehicles equipped with semi-automatic-gearboxes are tested by using the gears normally employed for driving, and the gear is used in accordance with the manufacturer's instructions. 2.3.3. Vehicles equipped with automatic gearboxes are tested with the highest gear (drive) engaged. The accelerator must be used in such a way as to obtain the steadiest acceleration possible, enabling the various gears to be engaged in the normal order. Furthermore, the gear-change points shown in Appendix 1 to this Annex do not apply; acceleration must continue throughout the period represented by the straight line connecting the end of each period of idling with the beginning of the next following period of steady speed. The tolerances given in 2.4 apply. 2.3.4. Vehicles equipped with an overdrive which the driver can activate are tested with the overdrive out of action for the urban cycle (Part One) and with the overdrive in action for the extra-urban cycle (Part Two). 2.3.5. At the request of the manufacturer, for a vehicle type where the idle speed of the engine is higher than the engine speed that would occur during operations 5, 12 and 24 of the elementary urban cycle (Part One), the clutch may be disengaged during the previous operation. 2.4.Tolerances 2.4.1. A tolerance of ± 2 km/h is allowed between the indicated speed and the theoretical speed during acceleration, during steady speed, and during deceleration when the vehicle's brakes are used. If the vehicle decelerates more rapidly without the use of the brakes, only the requirements of 6.5.3 apply. Speed tolerances greater than those prescribed are accepted during phase changes provided that the tolerances are never exceeded for more than 0,5 on any one occasion. 2.4.2. The time tolerances are ± 1,0 s. The above tolerances apply equally at the beginning and at the end of each gear changing periodIt should be noted that the time of two seconds allowed includes the time for changing gear and, if necessary, a certain amount of latitude to catch up with the cycle. for the urban cycle (Part One) and for the operations Nos 3, 5 and 7 of the extra-urban cycle (Part Two). 2.4.3. The speed and time tolerances are combined as indicated in Appendix 1. 3.VEHICLE AND FUEL 3.1.Test vehicle 3.1.1. The vehicle must be presented in good mechanical condition. It must have been run-in and driven at least 3000 kilometres before the test. 3.1.2. The exhaust device must not exhibit any leak likely to reduce the quantity of gas collected, which quantity must be that emerging from the engine. 3.1.3. The tightness of the intake system may be checked to ensure that carburation is not affected by an accidental intake of air. 3.1.4. The settings of the engine and of the vehicle's controls must be those prescribed by the manufacturer. This requirement also applies, in particular, to the settings for idling (rotation speed and carbon monoxide content of the exhaust gases), for the cold start device and for the exhaust gas pollutant emission control system. 3.1.5. The vehicle to be tested, or an equivalent vehicle, must be fitted, if necessary, with a device to permit the measurement of the characteristic parameters necessary for chassis dynamometer setting, in conformity with 4.1.1. 3.1.6. The technical service may verify that the vehicle's performance conforms to that stated by the manufacturer, that it can be used for normal driving and, more particularly, that it is capable of starting when cold and when hot. 3.2.Fuel When testing a vehicle against the emission limit values given in row A of the table in section 5.3.1.4 of Annex I to this Directive, the appropriate reference fuel must comply with the specifications given in section A of Annex IX or, in the case of gaseous reference fuels, either section A.1 or section B of Annex IXa.When testing a vehicle against the emission limit values given in row B of the table in section 5.3.1.4 of Annex I to this Directive, the appropriate reference fuel must comply with the specifications given in section B of Annex IX or, in the case of gaseous reference fuels, either section A.2 or section B of Annex IXa. 3.2.1. Vehicles that are fuelled either with petrol or with LPG or NG shall be tested according to Annex XII with the appropriate reference fuel(s) as defined in Annex IX a. 4.TEST EQUIPMENT 4.1.Chassis dynamometer 4.1.1. The dynamometer must be capable of simulating road load within one of the following classifications: dynamometer with fixed load curve, i.e. a dynamometer whose physical characteristics provide a fixed load curve shape, dynamometer with ajustable load curve, i.e. a dynamometer with at least two road load parameters that can be adjusted to shape the load curve. 4.1.2. The setting of the dynamometer must not be affected by the lapse of time. It must not produce any vibrations perceptible to the vehicle and likely to impair the vehicle's normal operations. 4.1.3. It must be equipped with means to simulate inertia and load. These simulators are connected to the front roller in the case of a two-roller dynamometer. 4.1.4.Accuracy 4.1.4.1. It must be possible to measure and read the indicated load to an accuracy of ± 5 %. 4.1.4.2. In the case of a dynamometer with a fixed load curve the accuracy of the load setting at 80 km/h must be ± 5 %. In the case of a dynamometer with an adjustable load curve, the accuracy of matching dynamometer load to road load must be 5 % at 120, 100, 80, 60 and 40, and 10 % at 20 km/h. Below this, dynamometer absorption must be positive. 4.1.4.3. The total inertia of the rotating parts (including the simulated inertia where applicable) must be known and must be within ± 20 kilograms of the inertia class for the test. 4.1.4.4. The speed of the vehicle must be measured by the speed of rotation of the roller (the front roller in the case of a two roller dynamometer). It must be measured with an accuracy of ± 1 km/h at speeds above 10 km/h. 4.1.5.Load and inertia setting 4.1.5.1. Dynamometer with fixed load curve: the load simulator must be adjusted to absorb the power exerted on the driving wheels at a steady speed of 80 km/h and the absorbed power at 50 km/h shall be noted. The means by which this load is determined and set are described in Appendix 3. 4.1.5.2. Dynamometer with adjustable load curve: the load simulator must be adjusted in order to absorb the power exerted on the driving wheels at steady speeds of 120, 100, 80, 60, 40 and 20 km/h. The means by which these loads are determined and set are described in Appendix 3. 4.1.5.3.Inertia Dynamometers with electrical inertia simulation must be demonstrated to be equivalent to mechanical inertia systems. The means by which equivalence is established is described in Appendix 4. 4.2.Exhaust-gas sampling system 4.2.1. The exhaust gas sampling system must be able to measure the actual quantities of pollutants emitted in the exhaust gases to be measured. The system to be used is the constant volume sampler (CVS) system. This requires that the vehicle exhaust be continuously diluted with ambient air under controlled conditions. In the constant volume sampler concept of measuring two conditions must be satisfied: the total volume of the mixture of exhaust gases and dilution air must be measured and a continuously proportional sample of the volume must be collected for analysis.The quantities of pollutants emitted are determined from the sample concentrations, corrected for the pollutant content of the ambient air and the totalized flow over the test period.The particulate pollutant emission level is determined by using suitable filters to collect the particulates from a proportional part flow throughout the test and determining the quantity thereof gravimetrically in accordance with 4.3.2. 4.2.2. The flow through the system must be sufficient to eliminate water condensation at all conditions which may occur during a test, as defined in Appendix 5. 4.2.3. Figure III.4.2.3 gives a schematic diagram of the general concept. Appendix 5 gives examples of three types of constant volume sampler system which satisfy the requirements set out in this Annex. 4.2.4. The gas and air mixture must be homogeneous at point S2 of the sampling probe. 4.2.5. The probe must extract a true sample of the diluted exhaust gases. 4.2.6. The system must be free of gas leaks. The design and materials must be such that the system does not influence the pollutant concentration in the diluted exhaust gas. Should any component (heat exchanger, blower, etc.) change the concentration of any pollutant gas in the diluted gas, the sampling for that pollutant must be carried out before that component if the problem cannot be corrected. 01970L0220-20070101_en_img_13 Diagram of exhaust gas sampling system 4.2.7. If the vehicle being tested is equipped with an exhaust pipe comprising several branches, the connecting tubes must be connected as near as possible to the vehicle but in such a manner so as not to effect the functioning of the vehicle. 4.2.8. Static pressure variations at the tailpipe(s) of the vehicle must remain within ± 1,25 kPa of the static pressure variations measured during the dynamometer driving cycle with no connection to the tailpipe(s). Sampling systems capable of maintaining the static pressure to within ± 0,25 kPa are used if a written request from a manufacturer to the competent authority issuing the approval substantiates the need for the narrower tolerance. The back-pressure must be measured in the exhaust pipe, as near as possible to its end or in an extension having the same diameter. 4.2.9. The various valves used to direct the exhaust gases must be of a quick-adjustment, quick-acting type. 4.2.10. The gas samples are collected in sample bags of adequate capacity. These bags must be made of such materials as will not change the pollutant gas by more than ± 2 % after 20 minutes of storage. 4.3.Analytical equipment 4.3.1.Requirements 4.3.1.1. Pollutant gases must be analyzed with the following instruments: Carbon monoxide (CO) and carbon dioxide (CO2) analysis:The carbon monoxide and carbon dioxide analysers must be of the non-dispersive infra-red (NDIR) absorption type. Hydrocarbons (HC) analysis — spark-ignition engines:The hydrocarbons analyser must be of the flame ionization (FID) type calibrated with propane gas expressed equivalent to carbon atoms (C1). Hydrocarbons (HC) analysis — compression-ignition engines:The hydrocarbons analyser must be of the flame ionization type with detector, valves, pipework, etc, heated to 463 K (190 °C) ± 10 K (HFID). It must be calibrated with propane gas expressed equivalent to carbon atoms (C1). Nitrogen oxide (NOx) analysis:The nitrogen oxide analyser must be either of the chemiluminescent (CLA) or of the non-dispensive ultraviolet resonance absorption (NDUVR) type, both with an NOx — NO converter. Particulates:Gravimetric determination of the particulates collected. These particulates are in each case collected by two series-mounted filters in the sample gas flow. The quantity of particulates collected by each pair of filters must be as follows:
Vep: flow through filters
Vmix: flow through tunnel
M: particulates mass (g/km)
Mlimit: limit mass of particulates (limit mass in force, g/km)
m: mass of particulates collected by filters (g)
d: actual distance corresponding to the operating cycle (km)
01970L0220-20070101_en_img_14 or 01970L0220-20070101_en_img_15
The particulates sample rate (Vep/Vmix) will be adjusted so that for M = Mlimit, 1 ≤ m ≤ 5 mg (when 47 mm diameter filters are used).
The filter surface consist of a material that is hydrophobic and inert towards the components of the exhaust gas (fluorocarbon-coated glass-fibre filters or equivalent).
4.3.1.2.Accuracy The analysers must have a measuring range compatible with the accuracy required to measure the concentrations of the exhaust gas sample pollutants. Measurement error must not exceed ± 2 % (intrinsic error of analyser) disregarding the true value for the calibration gases. For concentrations of less than 100 ppm the measurement error must not exceed ± 2 ppm. The ambient air sample msut be measured on the same analyser with an appropriate range. For concentrations of less than 100 ppm the measurement error must not exceed ± 3 ppm. The ambient air sample must be measured on the same analyser and range as the corresponding diluted exhaust sample. Measurement of the particulates collected shall be to a guaranteed accuracy of 1 μg. The microgram balance used to determine the weight of all filters must have an accuracy of 5 μg and readability of 1 μg. 4.3.1.3.Ice-trap No gas drying device must be used before the analysers unless shown to have no effect on the pollutant content of the gas stream.
4.3.2.Particular requirements for compression-ignition engines A heated sample line for a continuous HC-analysis with the flame ionization detector (HFID), including recorder (R) must be used. The average concentration of the measured hydrocarbons must be determined by integration. Throughout the test, the temperature of the heated sample line must be controlled at 463 K (190 °C) ± 10 K. The heated sampling line must be fitted with a heated filter (Fh) 99 % efficient with particle ≥ 0,3 μm to extract any solid particles from the continuous flow of gas required for analysis. The sampling system response time (from the probe to the analyser inlet) must be no more than four seconds.The HFID must be used with a constant flow (heat exchanger) system to ensure a representative sample, unless compensation for varying CFV or CFO flows is made.The particulate sampling unit consists of a dilution tunnel, a sampling probe, a filter unit, a partial-flow pump, and a flow rate regulator and measuring unit. The particulate-sampling part flow is drawn through two series-mounted filters. The sampling probe for the test gas flow for particulates must be so arranged within the dilution tract that a representative sample gas flow can be taken from the homogeneous air/exhaust mixture and an air/exhaust gas mixture temperature of 325 K (52 °C) is not exceeded immediately before the particulate filter.. The temperature of the gas flow in the flow meter may not fluctuate more than ± 3 K, nor may the mass flow-rate fluctuate by more than ± 5 %. Should the volume of flow change unacceptably as a result of excessive filter loading, the test must be stopped. When it is repeated, the rate of flow must be decreased and/or a larger filter used. The filters must be removed from the chamber no earlier than an hour before the test begins.The necessary particle filters must be conditioned (as regards temperature and humidity) in an open dish which has been protected against dust ingress for at least eight and for not more than 56 hours before the test in an air-conditioned chamber. After this conditioning the uncontaminated filters are weighed and stored until they are used.If the filters are not used within one hour of their removal from the weighing chamber they must be reweighed.The one-hour limit may be replaced by an eight-hour limit if one or both of the following conditions are met: a stabilized filter is placed and kept in a sealed filter holder assembly with the ends plugged, or a stabilized filter is placed in a sealed filter holder assembly which is then immediatly placed in a sample line through which there is no flow. 4.3.3.Calibration Each analyser must be calibrated as often as necessary and in any case in the month before type-approval testing and at least once every six months for verifying conformity of production. The calibration method to be used is described in Appendix 6 for the analysers referred to in 4.3.1.
4.4.Volume measurement 4.4.1. The method of measuring total dilute exhaust volume incorporated in the constant volume sampler must be such that measurement is accurate to ± 2 %. 4.4.2.Constant volume sampler calibration The constant volume sampler system volume measurement device must be calibrated by a method sufficient to ensure the prescribed accuracy and at a frequency sufficient to maintain such accuracy.An example of a calibration procedure which gives the required accuracy is given in Appendix 6. The method utilizes a flow metering device which is dynamic and suitable for the high flow-rate encountered in constant volume sampler testing. The device must be of certified accuracy in conformity with an approved national or international standard. 4.5.Gases 4.5.1.Pure gases The following pure gases must be available, if necessary, for calibration and operation: purified nitrogen(purity ≤ 1 ppm C, ≤ 1 ppm CO, ≤ 400 ppm CO2, ≤ 0,1 ppm NO), purified synthetic air(purity, ≤ 1 ppm C, ≤ 1 ppm CO, ≤ 400 ppm CO2, ≤ 0,1 ppm NO); oxygen content between 18 and 21 % vol, purified oxygen (purity ≤ 99,5 % vol O2), purified hydrogen (and mixture containing hydrogen)(purity ≤ 1 ppm C, ≤ 400 ppm CO2). 4.5.2.Calibration gases Gases having the following chemical compositions must be available: mixtures of: C3H8 and purified synthetic air (4.5.1), CO and purified nitrogen, CO2 and purified nitrogen, NO and purified nitrogen. (The amount of NO2 contained in this calibration gas must not exceed 5 % of the NO content).The true concentration of a calibration gas must be within ± 2 % of the stated figure.The concentrations specified in Appendix 6 may also be obtained by means of a gas divider, diluting with purified N2 or with purified synthetic air. The accuracy of the mixing device must be such that the concentrations of the diluted calibration gases may be determined to within ± 2 %. 4.6.Additional equipment 4.6.1.Temperatures The temperatures indicated in Appendix 8 are measured with an accuracy of ± 1,5 K. 4.6.2.Pressure The atmospheric pressure must be measurable to within ± 0,1 kPa. 4.6.3.Absolute humidity The absolute humidity (H) must be measurable to within ± 5 %. 4.7. The exhaust gas-sampling system must be verified by the method described in section 3 of Appendix 7. The maximum permissible deviation between the quantity of gas introduced and the quantity of gas measured is 5 %.
5.PREPARING THE TEST 5.1.Adjustment of inertia simulators to the vehicle's translatory inertia An inertia simulator is used enabling a total inertia of the rotating masses to be obtained proportional to the reference mass within the following limits:
Reference mass of vehicle RW(kg) Equivalent inertia I(kg)
RW ≤ 480 455
480 < RW ≤ 540 510
540 < RW ≤ 595 570
595 < RW ≤ 650 625
650 < RW ≤ 710 680
710 < RW ≤ 765 740
765 < RW ≤ 850 800
850 < RW ≤ 965 910
965 < RW ≤ 1080 1020
1080 < RW ≤ 1190 1130
1190 < RW ≤ 1305 1250
1305 < RW ≤ 1420 1360
1420 < RW ≤ 1530 1470
1530 < RW ≤ 1640 1590
1640 < RW ≤ 1760 1700
1760 < RW ≤ 1870 1810
1870 < RW ≤ 1980 1930
1980 < RW ≤ 2100 2040
2100 < RW ≤ 2210 2150
2210 < RW ≤ 2380 2270
2380 < RW ≤ 2610 2270
2610 < RW 2270
If the corresponding equivalent inertia is not available on the dynamometer, the larger value closest to the vehicle reference mass will be used.
5.2.Setting of dynamometer The load is adjusted according to methods described in 4.1.4.The method used and the values obtained (equivalent inertia — characteristic adjustment parameter) must be recorded in the test report. 5.3.Preconditioning of the vehicle 5.3.1. For compression-ignition engine vehicles for the purpose of measuring particulates at most 36 hours and at least six hours before testing, the Part Two cycle described in Appendix 1 must be used. Three consecutive cycles must be driven. The dynamometer setting is as indicated in 5.1 and 5.2. At the request of the manufacturer vehicles with positive ignition engine may be preconditioned with one Part I and two Part II driving cycles. After this preconditioning specific for compression ignition engines and before testing, compression-ignition and positive ignition engine vehicles must be kept in a room in which the temperature remains relatively constant between 293 and 303 K (20 and 30 °C). This conditioning must be carried out for at least six hours and continue until the engine oil temperature and coolant, if any, are within ± 2 K of the temperature of the room.If the manufacturer so requests, the test must be carried out not later than 30 hours after the vehicle has been run at its normal temperature. 5.3.1.1. For positive-ignition engined vehicles fuelled with LPG or NG or so equipped that they can be fuelled with either petrol or LPG or NG, between the tests on the first gaseous reference fuel and the second gaseous reference fuel, the vehicle shall be preconditioned before the test on the second reference fuel. This preconditioning is done on the second reference fuel by driving a preconditioning cycle consisting of one part one (urban part) and two times part two (extra-urban part) of the test cycle described in Appendix 1 to this Annex. On the manufacturer's request and with the agreement of the technical service this preconditioning cycle may be extended. The dynamometer setting shall be the one indicated in points 5.1 and 5.2 of this Annex. 5.3.2. The tyre pressures must be the same as that specified by the manufacturer and used for the preliminary road test for brake adjustment. The tyre pressures may be increased by up to 50 % from the manufacturer's recommended setting in the case of a two-roller dynamometer. The actual pressure used must be recorded in the test report.
6.PROCEDURE FOR BENCH TESTS 6.1.Special conditions for carrying out the cycle 6.1.1. During the test, the test cell temperature must be between 293 and 303 K (20 and 30 °C). The absolute humidity (H) of either the air in the test cell or the intake air of the engine must be such that:5,5 ≤ H ≤ 12,2 g H2O/kg dry air 6.1.2. The vehicle must be approximately horizontal during the test so as to avoid any abnormal distribution of the fuel. 6.1.3. A current of air of variable speed is blown over the vehicle. The blower speed shall be such that, within the operating range of 10 km/h to at least 50 km/h, the linear velocity of the air at the blower outlet is within ± 5 km/h of the corresponding roller speed. The final selection of the blower shall have the following characteristics: Area: at least 0,2 m2 Height of the lower edge above ground: approximately 20 cm Distance from the front of the vehicle: approximately 30 cm As an alternative the blower speed shall be at least 6m/s (21,6 km/h). At the request of the manufacturer for special vehicles (e.g. vans, off-road) the height of the cooling fan can be modified. 6.1.4. During the test the speed is recorded against time or collected by the data acquisition system so that the correctness of the cycles performed can be assessed. 6.2.Starting-up the engine 6.2.1. The engine must be started up by means of the devices provided for this purpose according to the manufacturer's instructions, as incorporated in the driver's handbook of production vehicles. 6.2.2. The first cycle starts on the initiation of the engine start-up procedure. 6.2.3. In the case of the use of LPG or NG as a fuel it is permissible that the engine is started on petrol and switched to LPG or NG after a predetermined period of time which cannot be changed by the driver. 6.3.Idling 6.3.1.Manual-shift or semi-automatic gearbox See Appendix tables III.1.2 and III.1.3. 6.3.1.1. During periods of idling the clutch must be engaged and the gears in neutral. 6.3.1.2. To enable the accelerations to be performed according to the normal cycle the vehicle must be placed in first gear, with the clutch disengaged, five seconds before the acceleration following the idling period considered of the elementary urban cycle (Part One). 6.3.1.3. The first idling period at the beginning of the urban cycle (Part One) consists of six seconds of idling in neutral with the clutch engaged and five seconds in first gear with the clutch disengaged.The two idling periods referred to above must be consecutiveThe idling period at the beginning of the extra-urban cycle (Part Two) consists of twenty seconds of idling in first gear with the clutch disengaged. 6.3.1.4. For the idling periods during each urban cycle (Part One) the corresponding times are 16 seconds in neutral and five seconds in first gear with the clutch disengaged. 6.3.1.5. The idling period between two successive elementary urban cycles (Part One) comprises 13 seconds in neutral with the clutch engaged. 6.3.1.6. At the end of the deceleration period (halt of the vehicle on the rollers) of the extra-urban cycle (Part Two), the idling period consists of twenty seconds in neutral with the clutch engaged. 6.3.2.Automatic-shift gearbox After initial engagement the selector must not be operated at any time during the test except as in the case specified in 6.4.3 or if the selector can actuate the overdrive, if any. 6.4.Accelerations 6.4.1. Accelerations must be so performed that the rate of acceleration is as constant as possible throughout the phase. 6.4.2. If an acceleration cannot be carried out in the prescribed time, the extra time required is, if possible, deducted from the time allowed for changing gear, but otherwise from the subsequent steady-speed period. 6.4.3.Automatic-shift gearboxes If an acceleration cannot be carried out in the prescribed time, the gear selector is operated in accordance with requirements for manual-shift gearboxes. 6.5.Deceleration 6.5.1. All decelerations of the elementary urban cycle (Part One) are effected by removing the foot completely from the accelerator, the clutch remaining engaged. The clutch is disengaged, without use of the gear lever, at a speed of 10 km/h.All the decelerations of the extra-urban cycle (Part Two) are effected by removing the foot completely from the accelerator, the clutch remaining engaged. The clutch is disengaged, without use of the gear lever, at a speed of 50 km/h for the last deceleration. 6.5.2. If the period of deceleration is longer than that prescribed for the corresponding phase, the vehicle's brakes are used to enable the timing of the cycle to be complied with. 6.5.3. If the period of deceleration is shorter than that prescribed for the corresponding phase, the timing of the theoretical cycle is restored by constant speed or idling period merging into the following operation. 6.5.4. At the end of the deceleration period (halt of the vehicle on the rollers) of the elementary urban cycle (Part One) the gears are placed in neutral and the clutch engaged. 6.6.Steady speeds 6.6.1. Pumping or the closing of the throttle must be avoided when passing from acceleration to the following steady speed. 6.6.2. Periods of constant speed are achieved by keeping the accelerator position fixed. 7.GAS AND PARTICULATE SAMPLING AND ANALYSIS 7.1.Sampling Sampling begins (BS) before or at the initiation of the engine start-up procedure and ends on conclusion of the final idling period in the extra-urban cycle (part two, end of sampling (ES)) or, in the case of test type VI of the final idling period of the last elementary cycle (part one). 7.2.Analysis 7.2.1. The exhaust gases contained in the bag must be analysed as soon as possible and in any event not later than 20 minutes after the end of the test cycle. The spent particulate filters must be taken to the chamber no later than one hour after conclusion of the test on the exhaust gases and must there be conditioned for between two and 36 hours and then be weighed. 7.2.2. Prior to each sample analysis the analyser range to be used for each pollutant must be set to zero with the appropriate zero gas. 7.2.3. The analysers are then set to the calibration curves by means of span gases of nominal concentrations of 70 to 100 % of the range. 7.2.4. The analysers' zeros are then rechecked. If the reading differs by more than 2 % of range from that set in 7.2.2, the procedure is repeated. 7.2.5. The samples are then analyzed. 7.2.6. After the analysis, zero and span points are rechecked using the same gases. If these rechecks are within 2 % of those in 7.2.3, the analysis is considered acceptable. 7.2.7. At all points in this section the flow-rates and pressures of the various gases must be the same as those used during calibration of the analysers. 7.2.8. The figure adopted for the concentration of each polluant measured in the gases is that read off after stabilization on the measuring device. Hydrocarbon mass emissions of compression-ignition engines are calculated from the integrated HFID reading, corrected for varying flow if necessary as shown in Appendix 5. 8.DETERMINATION OF THE QUANTITY OF GASEOUS AND PARTICULATE POLLUTANTS EMITTED 8.1.The volume considered The volume to be considered must be corrected to conform to the conditions of 101,33 kPa and 273,2 K. 8.2.Total mass of gaseous and particulate pollutants emitted The mass m of each gaseous pollutant emitted by the vehicle during the test is determined by obtaining the product of the volumetric concentration and the volume of the gas in question, with due regard to the following densities under the abovementioned reference conditions:
In the case of carbon monoxide (CO): d = 1.25 g/l
In the case of hydrocarbons:
for petrol (CH1.85) d = 0.619 g/l
for diesel (CH1.86) d = 0.619 g/l
for LPG (CH2.525) d = 0.649 g/l
for NG (CH4) d = 0.714 g/l
In the case of nitrogen oxides (NO2): d = 2.05 g/l
The mass m of particulate pollutant emissions from the vehicle during the test is defined by weighing the mass of particulates collected by the two filters, m1 by the first filter, m2 by the second filter: if 0,95 (m1 + m2) ≤ m1, m = m1, if 0,95 (m1 + m2) > m1, m = m1 + m2, if m2 > m1, the test is cancelled. Appendix 8 gives the calculations, followed by examples, used in determining the mass emissions of gaseous and particulate pollutants.
ANNEX IV TYPE II TEST(Carbon monoxide emission test at idling speed) 1.INTRODUCTION This Annex describes the procedure for the type II test defined in 5.3.2 of Annex I. 2.CONDITIONS OF MEASUREMENT 2.1. The fuel must be the reference fuel, specifications for which are given in Annex VIII. 2.2. During the test, the environmental temperature must be between 293 and 303 K (20 and 30 °C).The engine shall be warmed up until all temperatures of cooling and lubrication means and the pressure of lubrication means have reached equilibrium. 2.2.1. Vehicles that are fuelled either with petrol or with LPG or NG shall be tested with the reference fuel(s) used for the type I test. 2.3. In the case of vehicles with manually operated or semi-automatic-shift gearboxes the test must be carried out with the gear lever in the "neutral" position and with the clutch engaged. 2.4. In the case of vehicles with automatic gear-boxes the test is carried out with the gear selector in either the "neutral" or the "parking" position. 2.5.Components for adjusting the idling speed 2.5.1.Definition For the purposes of this Directive, "components for adjusting the idling speed" means controls for changing the idling conditions of the engine which may be easily operated by a mechanic using only the tools described in 2.5.1.1. In particular, devices for calibrating fuel and air flows are not considered as adjustment components if their setting requires the removal of the set-stops, an operation which cannot normally be performed except by a professional mechanic. 2.5.1.1. Tools which may be used to control components for adjusting the idling speed: screwdrivers (ordinary or cross-headed), spanners (ring, open-end or adjustable), pliers, Allen keys. 2.5.2.Determination of measurement points 2.5.2.1. A measurement at the setting in accordance with the conditions fixed by the manufacturer is performed first. 2.5.2.2. For each adjustment component with a continuous variation, a sufficient number of characteristic positions are determined. 2.5.2.3. The measurement of the carbon-monoxide content of exhaust gases must be carried out for all the possible positions of the adjustment components, but for components with a continuous variation only the positions defined in 2.5.2.2 are adopted. 2.5.2.4. The type II test is considered satisfactory if at least one of the two following conditions is met: 2.5.2.4.1. none of the values measured in accordance with 2.5.2.3 exceeds the limit values; 2.5.2.4.2. the maximum content obtained by continuously varying one of the adjustment components while the other components are kept stable does not exceed the limit value, this condition being met for the various combinations of adjustment components other than the one which was varied continuously. 2.5.2.5. The possible positions of the adjustment components are limited: 2.5.2.5.1. on the one hand, by the larger of the following two values: the lowest idling speed which the engine can reach; the speed recommended by the manufacturer, minus 100 revolutions per minute; 2.5.2.5.2. on the other hand, by the smallest of the following three values: the highest speed the engine can attain by activation of the idling speed components; the speed recommended by the manufacturer, plus 250 revolutions per minute; the cut-in speed of automatic clutches. 2.5.2.6. In addition, settings incompatible with correct running of the engine must not be adopted as measurement settings. In particular, when the engine is equipped with several carburettors all the carburettors must have the same setting. 3.SAMPLING OF GASES 3.1. The sampling probe is placed in the pipe connecting the exhaust with the sampling bag and as close as possible to the exhaust. 3.2. The concentration in CO (CCO) and CO2 (CCO2) is determined from the measuring instrument readings or recordings, by use of appropriate calibration curves. 3.3. The corrected concentration for carbon monoxide regarding four-stroke engines is: 01970L0220-20070101_en_img_16 (Vol. %) 3.4. The concentration in CCO (see 3.2) measured according to the formulae contained in 3.3 need not be corrected if the total of the concentrations measured (CCO + CCO2) is at least 15 for four-stroke engines. ANNEX V TYPE III TEST(Verifying emissions of crankcase gases) 1.INTRODUCTION This Annex describes the procedure for the type III test defined in section 5.3.3 of Annex I. 2.GENERAL PROVISIONS 2.1. The type III test is carried out on the vehicle with a positive-ignition engine which has been subjected to the type I or type III test as applicable. 2.2. The engines tested must include leak-proof engines other than those so designed that even a slight leak may cause unacceptable operating faults (such as flat-twin engines). 3.TEST CONDITIONS 3.1. Idling must be regulated in conformity with the manufacturer's recommendations. 3.2. The measurements are performed in the following three sets of conditions of engine operation:
Condition No Vehicle speed (km/h)
1 Idling
2 50 ± 2 (in 3rd gear or "drive")
3 50 ± 2 (in 3rd gear or "drive")
Condition No Power absorbed by brake
1 Nil
2 That corresponding to the settings for type I test at 50 km/h
3 That for conditions No 2, multiplied by a factor of 1,7
4.TEST METHOD 4.1. For the operation conditions as listed in 3.2 reliable function of the crankcase ventilation system must be checked. 5.METHOD OF VERIFICATION OF THE CRANKCASE VENTILATION SYSTEM (Refer also to Figure V.5.) 5.1. The engine's apertures must be left as found. 5.2. The pressure in the crankcase is measured at an appropriate location. It is measured at the dipstick hole with an inclined-tube manometer. 5.3. The vehicle is deemed satisfactory if, in every condition of measurement defined in 3.2, the pressure measured in the crankcase does not exceed the atmospheric pressure prevailing at the time of measurement. 5.4. For the test by the method described above, the pressure in the intake manifold is measured to within ± 1 kPa. 5.5 The vehicle speed as indicated at the dynamometer is measured to within ± 2 km/h. 5.6. The pressure measured in the crankcase is measured to within ± 0,01 kPa. 5.7. If in one of the conditions of measurement defined in 3.2 the pressure measured in the crankcase exceeds the atmospheric pressure, an additional test as defined in section 6 is performed if so requested by the manufacturer. 6.ADDITIONAL TEST METHOD 6.1. The engine's apertures must be left as found. 6.2. A flexible bag impervious to crankcase gases and having a capacity of approximately five litres is connected to the dipstick hole. The bag must be empty before each measurement. 6.3. The bag must be closed before each measurement. It must be opened to the crankcase for five minutes for each condition of measurement prescribed in 3.2. 6.4. The vehicle is deemed satisfactory if in every condition of measurement defined in 3.2 no visible inflation of the bag occurs. 6.5.Remark 6.5.1. If the structural layout of the engine is such that the test cannot be performed by the methods described in section 6, the measurements must be effected by that method modified as follows: 6.5.2. before the test, all apertures other than that required for the recovery of the gases are closed; 6.5.3. the bag is placed on a suitable take-off which does not introduce any additional loss of pressure and is installed on the recycling circuit of the device directly at the engine-connection aperture. 01970L0220-20070101_en_img_17 Type III test
ANNEX VI TYPE IV TESTTHE DETERMINATION OF EVAPORATIVE EMISSIONS FROM VEHICLES WITH SPARK-IGNITION ENGINES 1.INTRODUCTION This Annex describes the procedure for the Type IV test in accordance with section 5.3.4 of Annex I.This procedure describes a method for a determination of the loss of hydrocarbons by evaporation from the fuel systems of vehicles with positive-ignition engines. 2.DESCRIPTION OF TEST The evaporative emission test (Figure VI.1) is designed to determine hydrocarbon evaporative emissions as a consequence of diurnal temperatures fluctuation, hot soaks during parking, and urban driving. The test consists of these phases: test preparation including an urban (Part One) and extra-urban (Part Two) driving cycle, hot soak loss determination, diurnal loss determination. Mass emissions of hydrocarbons from the hot soak and the diurnal loss phases are added up to provide an overall result for the test. 3.VEHICLE AND FUEL 3.1.Vehicle 3.1.1. The vehicle must be in good mechanical condition and have been run in and driven at least 3000 km before the test. The evaporative emission control system must be connected and have been functioning correctly over this period and the carbon canister(s) must have been subject to normal use, neither undergoing abnormal purging nor abnormal loading. 3.2.Fuel 3.2.1. The appropriate reference fuel must be used, as defined in Annex IX to this Directive. 4.TEST EQUIPMENT FOR EVAPORATIVE TEST 4.1.Chassis dynamometer The chassis dynamometer must meet the requirements of Annex III. 4.2.Evaporative emission measurement enclosure The evaporative emission measurement enclosure must be a gas-tight rectangular measuring chamber able to contain the vehicle under test. The vehicle must be accessible from all sides and the enclosure when sealed must be gas tight in accordance with Appendix 1. The inner surface of the enclosure must be impermeable and non-reactive to hydrocarbons. The temperature conditioning system must be capable of controlling the internal enclosure air temperature to follow the prescribed temperature versus time profile throughout the test, and an average tolerance of ± 1 K over the duration of the test.The control system must be tuned to provide a smooth temperature pattern that has a minimum of overshoot, hunting, and instability about the desired long-term ambient temperature profile. Interior surface temperatures must not be less than 278 °K (5 °C) nor more than 320 °K (55 °C) at any time during the diurnal emission test.Wall design must be such as to promote good dissipation of heat. Interior surface temperatures must not be below 293 °K (20 °C), nor above 325 °K (52 °C) for the duration of the hot soak test.To accommodate the volume changes due to enclosure temperature changes, either a variable-volume or fixed-volume enclosure may be used. 4.2.1.Variable-volume enclosure The variable-volume enclosure expands and contracts in response to the temperature change of the air mass in the enclosure. Two potential means of accommodating the internal volume changes are movable panel(s), or a bellows design, in which an impermeable bag or bags inside the enclosure expand(s) and contracts(s) in response to internal pressure changes by exchanging air from outside the enclosure. Any design for volume accommodation must maintain the integrity of the enclosure as specified in Appendix 1 over the specified temperature range.Any method of volume accommodation must limit the differential between the enclosure internal pressure and the barometric pressure to a maximum value of ± 5 hPa.The enclosure must be capable of latching to a fixed volume. A variable volume enclosure must be capable of accommodating a ± 7 % change from its "nominal volume" (see Appendix 1 section 2.1.1), taking into account temperature and barometric pressure variation during testing. 4.2.2.Fixed-volume enclosure The fixed-volume enclosure must be constructed with rigid panels that maintain a fixed enclosure volume, and meet the requirements below. 4.2.2.1. The enclosure must be equipped with an outlet flow stream that withdrawns air at a low, constant rate from the enclosure throughout the test. An inlet flow stream may provide make-up air to balance the outgoing flow with incoming ambient air. Inlet air must be filtered with activated carbon to provide a relatively constant hydrocarbon level. Any method of volume accommodation must maintain the differential between the enclosure internal pressure and the barometric pressure between 0 and -5 hPa. 4.2.2.2. The equipment must be capable of measuring the mass of hydrocarbon in the inlet and outlet flow streams with a resolution of 0,01 gram. A bag sampling system may be used to collect a proportional sample of the air withdrawn from and admitted to the enclosure. Alternatively, the inlet and outlet flow streams may be continuously analysed using an on-line FID analyser and integrated with the flow measurements to provide a continuous record of the mass hydrocarbon removal. 4.3.Analytical systems 4.3.1.Hydrocarbon analyser 4.3.1.1. The atmosphere within the chamber is monitored using a hydrocarbon detector of the flame ionization detector (FID) type. Sample gas must be drawn from the mid-point of one side wall or roof of the chamber and any bypass flow must be returned to the enclosure, preferably to a point immediately downstream of the mixing fan. 4.3.1.2. The hydrocarbon analyser must have a response time to 90 % of final reading of less than 1,5 seconds. Its stability must be better than 2 % of full scale at zero and at 80 % ± 20 % of full scale over a 15-minute period for all operational ranges. 4.3.1.3. The repeatability of the analyser expressed as one standard deviation must be better than 1 % of full scale deflection at zero and at 80 % ± 20 % of full scale on all ranges used. 4.3.1.4. The operational ranges of the analyser must be chosen to give best resolution over the measurement, calibration and leak checking procedures. 4.3.2.Hydrocarbon analyser data recording system 4.3.2.1. The hydrocarbon analyser must be fitted with a device to record electrical signal output either by strip chart recorder or other data processing system at a frequency of at least once per minute. The recording system must have operating characteristics at least equivalent to the signal being recorded and must provide a permanent record of results. The record must show a positive indication of the beginning and end of the hot soak or diurnal emission test (including beginning and end of sampling periods along with the time elapsed between start and completion of each test). 01970L0220-20070101_en_img_18 Note: 1.Evaporative emission control families — details clarified. 2.Tailpipe emissions may be measured during type I test drive, but these are not used for legislative purposes. Exhaust emission legislative test remains separate. 4.4.Fuel tank heating (only applicable for gasoline canister load option) 4.4.1. The fuel in the vehicle tank(s) must be heated by a controllable source of heat; for example a heating pad of 2000 W capacity is suitable. The heating system must apply heat evenly to the tank walls beneath the level of the fuel so as not to cause local overheating of the fuel. Heat must not be applied to the vapour in the tank above the fuel. 4.4.2. The tank heating device must make it possible to heat the fuel in the tank evenly by 14 °K from 289 °K (16 °C) within 60 minutes, with the temperature sensor position as in 5.1.1. The heating system must be capable of controlling the fuel temperature to ± 1,5 °K of the required temperature during the tank heating process. 4.5.Temperature recording 4.5.1. The temperature in the chamber is recorded at two points by temperature sensors which are connected so as to show a mean value. The measuring points are extended approximately 0,1 m into the enclosure from the vertical centre line of each side wall at a height of 0,9 ± 0,2 m. 4.5.2. The temperatures of the fuel tank(s) are recorded by means of the sensor positioned in the fuel tank as in 5.1.1 in the case of use of the gasoline canister load option (5.1.5). 4.5.3. Temperatures must, throughout the evaporative emission measurements, be recorded or entered into a data processing system at a frequency of at least once per minute. 4.5.4. The accuracy of the temperature recording system must be within ± 1,0 °K and the temperature must be capable of being resolved to ± 04, °K. 4.5.5. The recording or data processing system must be capable of resolving time to ± 15 seconds. 4.6.Pressure recording 4.6.1. The difference Δp between barometric pressure within the test area and the enclosure internal pressure must, throughout the evaporative emission measurements, be recorded or entered into a data processing system at a frequency of at least once per minute. 4.6.2. The accuracy of the pressure recording system must be within ± 2 hPa and the pressure must be capable of being resolved to ± 0,2 hPa. 4.6.3. The recording or data processing system must be capable of resolving time to ± 15 seconds. 4.7.Fans 4.7.1. By the use of one or more fans or blowers with the SHED door(s) open it must be possible to reduce the hydrocarbon concentration in the chamber to the ambient hydrocarbon level. 4.7.2. The chamber must have one or more fans or blowers of likely capacity 0,1 to 0,5 m3s-1 with which to thoroughly mix the atmosphere in the enclosure. It must be possible to attain an even temperature and hydrocarbon concentration in the chamber during measurements. The vehicle in the enclosure must not be subjected to a direct stream of air from the fans or blowers. 4.8.Gases 4.8.1. The following pure gases must be available for calibration and operation: purified synthetic air (purity: < 1 ppm C1 equivalent ≤ 1 ppm CO, ≤ 400 ppm CO2, ≤ 0,1 ppm NO); oxygen content between 18 % and 21 % by volume, hydrocarbon analyser fuel gas (40 % ± 2 % hydrogen, and balance helium with less than 1 ppm C1 equivalent hydrocarbon, less than 400 ppm CO2), propane (C3H8), 99,5 % minimum purity, butane (C4H10), 98 % minimum purity, nitrogen (N2), 98 % minimum purity. 4.8.2. Calibration and span gases must be available containing mixtures of propane (C3H8) and purified synthetic air. The true concentrations of a calibration gas must be within ± 2 % of stated figures. The accuracy of the diluted gases obtained when using a gas divider must be to within ± 2 % of the true value. The concentrations specified in Appendix 1 may also be obtained by the use of a gas divider using synthetic air as the diluent gas. 4.9.Additional equipment 4.9.1. The absolute humidity in the tests area must be measurable to within ± 5 %. 5.TEST PROCEDURE 5.1.Test preparation 5.1.1. The vehicle is mechanically prepared before the test as follows: the exhaust system of the vehicle must not exhibit any leaks, the vehicle may be steam cleaned before the test, in the case of use of the gasoline canister load option (5.1.5) the fuel tank of the vehicle must be equipped with a temperature sensor to enable the temperature to be measured at the mid-point of the fuel in the fuel tank when filled to 40 % of its capacity, additional fittings, adapters of devices may be fitted to the fuel system in order to allow a complete draining of the fuel tank. For this purpose it is not necessary to modify the shell of the tank, the manufacturer may propose a test method in order to take into account the loss of hydrocarbons by evaporation coming only from the fuel system of the vehicle. 5.1.2. The vehicle is taken into the test area where the ambient temperature is between 293 °K and 303 °K (20 and 30 °C). 5.1.3. The ageing of the canister(s) has to be verified. This may be done by demonstrating that it has accumulated a minimum of 3000 km. If this demonstration is not given, the following procedure is used. In the case of a multiple canister system each canister must undergo the procedure separately. 5.1.3.1. The canister is removed from the vehicle. Special care must be taken during this step to avoid damage to components and the integrity of the fuel system. 5.1.3.2. The weight of the canister must be checked. 5.1.3.3. The canister is connected to a fuel tank, possibly an external one, filled with reference fuel, to 40 % volume of the fuel tank(s). 5.1.3.4. The fuel temperature in the fuel tank must be between 283 °K (10 °C) and 287 °K (14 °C). 5.1.3.5. The (external) fuel tank is heated from 288 °K to 318 °K (15 ° to 45 °C) (1 °C increase every 9 minutes). 5.1.3.6. If the canister reaches breakthrough before the temperature reaches 318 °K (45 °C), the heat source must be turned off. Then the canister is weighed. If the canister did not reach breakthrough during the heating to 318 °K (45° °C), the procedure from 5.1.3.3 must be repeated until breakthrough occurs. 5.1.3.7. Breakthrough may be checked as is described in 5.1.5 and 5.1.6 of this Annex, or with the use of another sampling and analytical arrangement capable of detecting the emission of hydrocarbons from the canister at breakthrough. 5.1.3.8. The canister must be purged with 25 ± 5 litres per minute with the emission laboratory air until 300 bed volume exchanges are reached. 5.1.3.9. The weight of the canister must be checked. 5.1.3.10. The steps of the procedure in 5.1.3.4 to 5.1.3.9 must be repeated nine times. The test may be terminated prior to that, after not less than three ageing cycles, if the weight of the canister after the last cycles has stabilized. 5.1.3.11. The evaporative emission canister is reconnected and the vehicle restored to its normal operating condition. 5.1.4. One of the methods specified in 5.1.5 and 5.1.6 must be used to precondition the evaporative canister. For vehicles with multiple canisters, each canister must be preconditioned separately. 5.1.4.1. Canister emissions are measured to determine breakthrough.Breakthrough is here defined as the point at which the cumulative quantity of hydrocarbons emitted is equal to 2 grams. 5.1.4.2. Breakthrough may be verified using the evaporative emission enclosure as described in 5.1.5 and 5.1.6 respectively. Alternatively, breakthrough may be determined using an auxiliary evaporative canister connected downstream of the vehicle's canister. The auxiliary canister must be well purged with dry air prior to loading. 5.1.4.3. The measuring chamber must be purged for several minutes immediately before the test until a stable background is obtained. The chamber air mixing fan(s) must be switched on at this time.The hydrocarbon analyser must be zeroed and spanned immediately before the test. 5.1.5.Canister loading with repeated heat builds to breakthrough 5.1.5.1. The fuel tank(s) of the vehicle(s) is (are) emptied using the fuel tank drain(s). This must be done so as not to abnormally purge or abnormally load the evaporative control devices fitted to the vehicle. Removal of the fuel cap is normally sufficient to achieve this. 5.1.5.2. The fuel tank(s) is (are) refilled with test fuel at a temperature of between 283 °K to 287 °K (10 to 14 °C) to 40 % ± 2 % of the tank's normal volumetric capacity. The fuel cap(s) of the vehicle must be fitted at this point. 5.1.5.3. Within one hour of being refuelled the vehicle must be placed, with the engine shut off, in the evaporative emission enclosure. The fuel tank temperature sensor is connected to the temperature recording system. A heat source must be properly positioned with respect to the fuel tank(s) and connected to the temperature controller. The heat source is specified in 4.4. In the case of vehicles fitted with more than one fuel tank, all the tanks must be heated in the same way as described below. The temperatures of the tanks must be identical to within ± 1,5 °K. 5.1.5.4. The fuel may be artificially heated to the starting diurnal temperature of 293 °K (20 °C) ± 1 °K. 5.1.5.5. When the fuel temperature reaches at last 292 °K (19 °C), the following steps must be taken immediately: the purge blower must be turned off; enclosure doors closed and sealed; and measurement initiated of the hydrocarbon level in the enclosure. 5.1.5.6. When the fuel temperature of the fuel tank reaches 293 °K (20 °C) a linear heat build of 15 °K (15 °C) begins. The fuel must be heated in such a way that the temperature of the fuel during the heating conforms to the function below to within ± 1,5 °K. The elapsed time of the heat build and temperature rise is recorded.Tr = T0 + 0,2333 × twhere: Trrequired temperature (K); Toinitial temperature (K); ttime from start of the tank heat build in minutes. 5.1.5.7. As soon as breakthrough occurs or when the fuel temperature reaches 308 °K (35 °C), whichever occurs first, the heat source is turned off, the enclosure doors unsealed and opened, and the vehicle fuel tank cap(s) removed. If breakthrough has not occurred by the time the fuel temperature 308 °K (35 °C), the heat source is removed from the vehicle, the vehicle removed from the evaporative emission enclosure and the entire procedure outlined in 5.1.7 repeated until breakthrough occurs. 5.1.6.Butane loading to breakthrough 5.1.6.1. If the enclosure is used for the determination of the breakthrough (see 5.1.4.2) the vehicle must be placed, with the engine shut off, in the evaporative emission enclosure. 5.1.6.2. The evaporative emission canister must be prepared for the canister loading operation. The canister must not be removed from the vehicle, unless access to it in its normal location is so restricted that loading can only reasonably be accomplished by removing the canister from the vehicle. Special care must be taken during this step to avoid damage to the components and the integrity of the fuel system. 5.1.6.3. The canister is loaded with a mixture composed of 50 % butane and 50 % nitrogen by volume at a rate of 40 grams butane per hour. 5.1.6.4. As soon as the canister reaches breakthrough, the vapour source must be shut off. 5.1.6.5. The evaporative emission canister must then be reconnected and the vehicle restored to its normal operating condition. 5.1.7.Fuel drain and refill 5.1.7.1. The fuel tank(s) of the vehicle(s) is (are) emptied using the fuel tank drain(s). This must be done so as not to abnormally purge or abnormally load the evaporative control devices fitted to the vehicle. Removal of the fuel cap is normally sufficient to achieve this. 5.1.7.2. The fuel tank(s) is (are) refilled with test fuel at a temperature of between 291 °K ± 8 °K (18 ± 8 °C) to 40 ± 2 % of the tank's normal volumetric capacity. The fuel cap(s) of the vehicle must be fitted at this point. 5.2.Preconditioning drive 5.2.1. Within one hour from the completing of canister loading in accordance with 5.1.5 or 5.1.6 the vehicle is placed on the chassis dynamometer and driven through one Part One and two Part Two driving cycles of Type I test as specified in Annex III. Exhaust emissions are not sampled during this operation. 5.3.Soak 5.3.1. Within five minutes of completing the preconditioning operation specified in 5.2.1 the engine bonnet must be completely closed and the vehicle driven off the chassis dynamometer and parked in the soak area. The vehicle is parked for a minimum of 12 hours and a maximum of 36 hours. The engine oil and coolant temperatures must have reached the temperature of the area or within ± 3 °K of it at the end of the period. 5.4.Dynamometer test 5.4.1. After conclusion of the soak period the vehicle is driven through a complete Type I test drive as described in Annex III (cold start urban and extra urban test). Then the engine is shut off. Exhaust emissions may be sampled during this operation but the results must not be used for the purpose of exhaust emission type-approval. 5.4.2. Within two minutes of completing the Type I test drive specified in 5.4.1 the vehicle is driven a further conditioning drive consisting of one urban test cycle (hot start) of a Type I test. Then the engine is shut off again. Exhaust emissions need not be sampled during this operation. 5.5.Hot soak evaporative emissions test 5.5.1. Before the completion of the conditioning drive the measuring chamber must be purged for several minutes until a stable hydrocarbon background is obtained. The enclosure mixing fan(s) must also be turned on at this time. 5.5.2. The hydrocarbon analyser must be zeroed and spanned immediately prior to the test. 5.5.3. At the end of the conditioning drive the engine bonnet must be completely closed and all connections between the vehicle and the test stand disconnected. The vehicle is then driven to the measuring chamber with a minimum use of the accelerator pedal. The engine must be turned off before any part of the vehicle enters the measuring chamber. The time at which the engine is switched off is recorded on the evaporative emission measurement data recording system and temperature recording begins. The vehicle's windows and luggage compartments must be opened at this stage, if not already opened. 5.5.4. The vehicle must be pushed or otherwise moved into the measuring chamber with the engine switched off. 5.5.5. The enclosure doors are closed and sealed gas-tight within two minutes of the engine being switched off and within seven minutes of the end of the conditioning drive. 5.5.6. The start of a 60 ± 0,5 minute hot soak period begins when the chamber is sealed. The hydrocarbon concentration, temperature and barometric pressure are measured to give the initial readings CHC,i Pi and Ti for the hot soak test. These figures are used in the evaporative emission calculation, section 6. The ambient SHED temperature T must not be less than 296 °K and no more than 304 °K during the 60-minute hot soak period. 5.5.7. The hydrocarbon analyser must be zeroed and spanned immediately before the end of the 60 ± 0,5 minute test period. 5.5.8. At the end of the 60 ± 0,5 minute test period the hydrocarbon concentration in the chamber must be measured. The temperature and the barometric pressure are also measured. These are the final readings CHC,f, Pf and Tf for the hot soak test used for the calculation in section 6. 5.6.Soak 5.6.1. The test vehicle must be pushed or otherwise moved to the soak area without use of the engine and soaked for not less than 6 hours and not more than 36 hours between the end of the hot soak test and the start of the diurnal emission test. For at least 6 hours of this period the vehicle must be soaked at 293 °K ± 2 °K (20 °C ± 2 °C). 5.7.Diurnal test 5.7.1. The test vehicle must be exposed to one cycle of ambient temperature according to the profile specified in Appendix 2 with a maximum deviation of ± 2 °K at any time. The average temperature deviation from the profile, calculated using the absolute value of each measured deviation, must not exceed 1 °K. Ambient temperature must be measured at least every minute. Temperature cycling begins when time tstart = 0, as specified in 5.7.6. 5.7.2. The measuring chamber must be purged for several minutes immediately before the test until a stable background is obtainable. The chamber mixing fan(s) must also be switched on at this time. 5.7.3. The test vehicle, with the engine shut off and the test vehicle windows and luggage compartment(s) opened must be moved into the measuring chamber. The mixing fan(s) must be adjusted in such a way as to maintain a minimum air circulation of 8 km/h under the fuel tank of the test vehicle. 5.7.4. The hydrocarbon analyser must be zeroed and spanned immediately before the test. 5.7.5. The enclosure doors must be closed and gas-tight sealed. 5.7.6. Within 10 minutes of closing and sealing the doors, the hydrocarbon concentration, temperature and barometric pressure are measured to give the initial readings CHC,i, Pf and Tf for the diurnal test. This is the point where time tStart = 0. 5.7.7. The hydrocarbon analyser must be zeroed and spanned immediately before the end of the test. 5.7.8. The end of the emission sampling period occurs 24 hours ± 6 minutes after the beginning of the initial sampling, as specified in 5.7.6. The time elapsed is recorded. The hydrocarbon concentration, temperature and barometric pressure are measured to give the final readings CHC,i, Pf and Tf for the diurnal test used for the calculation in section 6. This completes the evaporative emission test procedure. 6.CALCULATION 6.1. The evaporative emission tests described in section 5 allow the hydrocarbon emissions from the diurnal and hot soak phases to be calculated. Evaporative losses from each of theses phases is calculated using the initial and final hydrocarbon concentrations, temperatures and pressures in the enclosure, together with the net enclosure volume.The formula below is used: 01970L0220-20070101_en_img_19where: MHChydrocarbon mass in grams MHC,outmass of hydrocarbon exiting the enclosure, in the case of fixed-volume enclosures for diurnal emission testing (grams). MHC,imass of hydrocarbon entering the enclosure, in the case of fixed-volume enclosures for diurnal emission testing (grams). CHCmeasured hydrocarbon concentration in the enclosure (ppm (volume) C1 equivalent), Vnet enclosure volume in cubic metres corrected for the volume of the vehicle, with the windows and the luggage compartment open. If the volume of the vehicle is not determined a volume of 1,42 m3 is subtracted. Tambient chamber temperature, in °K, Pbarometric pressure in kPA, H/Chydrogen to carbon ration, k1,2 · (12 + H/C); where: iis the initial reading, fis the final reading, H/Cis taken to be 2,33 for diurnal test losses, H/Cis taken to be 2,20 for hot soak losses. 6.2.Overall results of test The overall hydrocarbon mass emission for the vehicle is taken to be:Mtotal = MDI + MHSwhere: Mtotaloverall mass emissions of the vehicle (grams), MDIhydrocarbon mass emission for diurnal test (grams), MHShydrocarbon mass emission for the hot soak (grams). 7.CONFORMITY OF PRODUCTION 7.1. For routine end-of-production-line testing, the holder of the approval may demonstrate compliance by sampling vehicles which shall meet the following requirements. 7.2.Test for leakage 7.2.1. Vents to the atmosphere from the emission control system shall be isolated. 7.2.2. A pressure of 370 ± 10 mm of H2O must be applied to the fuel system. 7.2.3. The pressure must be allowed to stabilize prior to isolating the fuel system from the pressure source. 7.2.4. Following isolation of the fuel system, the pressure must not drop by more than 50 mm of H2O in five minutes. 7.3.Test for venting 7.3.1. Vents to the atmosphere from the emission control must be isolated. 7.3.2. A pressure of 370 ± 10 mm of H2O must be applied to the fuel system. 7.3.3. The pressure must be allowed to stabilize prior to isolating the fuel system from the pressure source. 7.3.4. The venting outlets from the emission control systems to the atmosphere must be reinstated to the production condition. 7.3.5. The pressure of the fuel system must drop to below 100 mm of H2O in not less than 30 seconds but within two minutes. 7.3.6. At the request of the manufacturer the functional capacity for venting can be demonstrated by equivalent alternative procedure. The specific procedure should be demonstrated by the manufacturer to the technical service during the type approval procedure. 7.4.Purge test 7.4.1. Equipment capable of detecting an airflow rate of 1,0 litres in one minute must be attached to the purge inlet and a pressure vessel of sufficient size to have negligible effect on the purge system must be connected via a switching valve to the purge inlet, or alternatively, 7.4.2. the manufacturer may use a flow meter of his own choice, if acceptable to the competent authority. 7.4.3. The vehicle must be operated in such a manner that any design feature of the purge system that could restrict purge operation is detected and the circumstances noted. 7.4.4. Whilst the engine is operating within the bounds noted in 7.4.3, the air flow must be determined by either: 7.4.4.1. the device indicated in 7.4.1 being switched in. A pressure drop from atmospheric to a level indicating that a volume of 1,0 litres of air has flowed into the evaporative emission control system within one minute must be observed; or 7.4.4.2. if an alternative flow measuring device is used, a reading of no less than 1,0 litre per minute must be detectable. 7.4.4.3. At the request of the manufacturer an alternative purge test procedure can be used, if the procedure has been presented to and has been accepted by the technical service during the type approval procedure. 7.5. The competent authority which has granted type-approval may at any time verify the conformity control methods applicable to each production unit. 7.5.1. The inspector must take a sufficiently large sample from the series. 7.5.2. The inspector may test these vehicles by application of either 7.1.4 or 7.1.5 of Annex I. 7.5.3. If in pursuance of section 7.1.5 of Annex I the vehicle's test result falls outside the agreed limits of section 5.3.4.2 of Annex I, the manufacturer may request that the approval procedure referred to in 7.1.4 of Annex I be applied. 7.5.3.1. The manufacturer must not be allowed to adjust, repair or modify any of the vehicles, unless they failed to comply with the requirements of section 7.1.4 of Annex I and unless such work is documented in the manufacturer's vehicle assembly and inspection procedures. 7.5.3.2. The manufacturer may request a single re-test for a vehicle whose evaporative emission characteristics are likely to have changed due to his actions under 7.5.3.1. 7.6. If the requirements of 7.5 are not met, the competent authority must ensure that all necessary steps are taken to re-establish conformity of production as rapidly as possible. ANNEX VII TYPE VI TEST(Verifying the average low ambient temperature carbon monoxide and hydrocarbon tailpipe emissions after a cold start) 1.INTRODUCTION This Annex applies only to vehicles with positive-ignition engines as defined in section 5.3.5. of Annex I. It describes the equipment required and the procedure for the Type VI test defined in section 5.3.5 of Annex I in order to verify the emissions of carbon monoxide and hydrocarbons at low ambient temperatures. Topics addressed in this Annex include: 1.Equipment requirements; 2.Test conditions; 3.Test procedures and data requirements. 2.TEST EQUIPMENT 2.1.Summary 2.1.1. This chapter deals with the equipment needed for low ambient temperature exhaust emission tests on vehicles equipped with positive-ignition engines, as defined in section 5.3.5. of Annex I. Equipment required and specifications are equivalent to the requirements for the Type I test as specified in Annex III, with appendices, if specific requirements for the Type VI test are not prescribed. Sections 2.2 to 2.6 describe deviations applicable to Type VI low ambient temperature testing. 2.2.Chassis dynamometer 2.2.1. The requirements of section 4.1 of Annex III apply. The dynamometer must be adjusted to simulate the operation of a vehicle on the road at 266 °K (-7 ° C). Such adjustment may be based on a determination of the road load force profile at 266 °K (-7 ° C). Alternatively the driving resistance determined according to Appendix 3 of Annex III may be adjusted for a 10 % decrease of the coast-down time. The technical service may approve the use of other methods of determining the driving resistance. 2.2.2. For calibration of the dynamometer the provisions of Appendix 2 of Annex III apply. 2.3.Sampling system 2.3.1. The provisions of section 4.2 of Annex III and Appendix 5 of Annex III apply. Section 2.3.2 in Appendix 5 is modified to read: "The piping configuration, flow capacity of the CVS, and the temperature and specific humidity of the dilution air (which may be different from the vehicle combustion air source) must be controlled so as to virtually eliminate water condensation in the system (a flow of 0,142 to 0,165 m2/s is sufficient for most vehicles)." 2.4.Analytical equipment 2.4.1. The provisions of section 4.3 of Annex III apply, but only for carbon monoxide, carbon dioxide, and hydrocarbon testing. 2.4.2. For calibrations of the analytical equipment the provisions of Appendix 6 of Annex III apply. 2.5.Gases 2.5.1. The provisions of section 4.5 of Annex III apply, where they are relevant. 2.6.Additional equipment 2.6.1. For equipment used for the measurement of volume, temperature, pressure and humidity the provisions in sections 4.4 and 4.6 of Annex III apply. 3.TEST SEQUENCE AND FUEL 3.1.General requirements 3.1.1. The test sequence in Figure VII.1 shows the steps encountered as the test vehicle undergoes the procedures for the Type VI test. Ambient temperature levels encountered by the test vehicle must average: 266 °K (-7 °C) ± 3 °K and must:not be less than 260 °K (-13 °C), no more than 272 °K (-1 °C).The temperature may:not fall below 263 °K (-10 °C), or exceed 269 °K (-4 °C)for more than three consecutive minutes. 3.1.2. The test cell temperature monitored during testing must be measured at the output of the cooling fan (section 5.2.1 of this Annex). The ambient temperature reported must be an arithmetic average of the test cell temperatures measured at constant intervals no more than one minute apart. 3.2.Test procedure The part one urban driving cycle according to Figure III.1.1 in Annex III - Appendix 1, consists of four elementary urban cycles which together makes a complete part one cycle. 3.2.1. Start of engine, start of the sampling and the operation of the first cycle must be in accordance with Table III.1.2 and Figure III.1.2. 3.3.Preparation for the test 3.3.1. For the test vehicle the provisions of section 3.1 of Annex III apply. For setting the equivalent inertia mass on the dynamometer the provisions of section 5.1 of Annex III apply. 01970L0220-20070101_en_img_20 3.4.Test fuel 3.4.1. The test fuel must comply with the specifications given in section C of Annex IX. 4.VEHICLE PRECONDITIONING 4.1.Summary 4.1.1. To ensure reproducible emission tests, the test vehicles must be conditioned in a uniform manner. The conditioning consists of a preparatory drive on a chassis dynamometer followed by a soak period before the emission test according to 4.3. 4.2.Preconditioning 4.2.1. The fuel tank(s) must be filled with the specified test fuel. If the existing fuel in the fuel tank(s) does not meet the specifications contained in 3.4.1, the existing fuel must be drained prior to the fuel fill. The test fuel must be at a temperature less than or equal to 289 °K (+ 16 °C). For the above operations the evaporative emission control system must neither be abnormally purged nor abnormally loaded. 4.2.2. The vehicle is moved to the test cell and placed on the chassis dynamometer. 4.2.3. The preconditioning consists of the driving cycle according to Annex III — Appendix 1 Figure III.1.1, parts one and two. At the request of the manufacturer, vehicles with a positive-ignition engine may be preconditioned with one Part I and two Part II driving cycles. 4.2.4. During the preconditioning the test cell temperature must remain relatively constant and not be higher than 303 °K (30 °C). 4.2.5. The drive-wheel tyre pressure must be set in accordance with the provisions of section 5.3.2 of Annex III. 4.2.6. Within ten minutes of completion of the preconditioning, the engine must be switched off. 4.2.7. If requested by the manufacturer and approved by the technical service, additional preconditioning may in exceptional cases be allowed. The technical service may also choose to conduct additional preconditioning. The additional preconditioning consists of one or more driving schedules of the part one cycle as described in Annex III — Appendix 1. The extent of such additional preconditioning must be recorded in the test report. 4.3.Soak methods 4.3.1. One of the following two methods, to be selected by the manufacturer, must be utilized to stabilize the vehicle before the emission test. 4.3.2. Standard method. The vehicle is stored for not less than 12 hours nor for more than 36 hours prior to the low ambient temperature tailpipe emission test. The ambient temperature (dry bulb) during this period must be maintained at an average termperature of: 266 °K (-7 °C) ± 3 °K during each hour of this period and must not be less than 260 °K (-13 °C) nor more than 272 (-1 °C). In addition, the temperature may not fall below 263 °K (-10 °C) nor more than 269 °K (-4 °C) for more than three consecutive minutes. 4.3.3. Forced methodThe provisions concerning "forced cool down methods" must be re-examined without delay in accordance with the procedure laid down in Article 13 of Directive 70/156/EEC.. The vehicle must be stored for not more than 36 hours prior to the low ambient temperature tailpipe emission test. 4.3.3.1. The vehicle must not be stored at ambient temperatures which exceed 303 °K (30 °C) during this period. 4.3.3.2. Vehicle cooling may be accomplished by force-cooling the vehicle to the test temperature. If cooling is augmented by fans, the fans must be placed in a vertical position so that the maximum cooling of the drive train and engine is achieved and not primarily the sump. Fans must not be placed under the vehicle. 4.3.3.3. The ambient temperature need only be stringently controlled after the vehicle has been cooled to:266 °K (-7 °C) ± 2 °K,as determined by a representative bulk oil temperature. A representative bulk oil temperature is the temperature of the oil measured near the middle of the oil, not at the surface or at the bottom of the oil sump. If tow or more diverse locations in the oil are monitored, they must all meet the temperature requirements. 4.3.3.4. The vehicle must be stored for at least one hour after is has been cooled to 266 °K (-7 °C) ± 2 °K, prior to the low ambient temperature tailpipe emission test. The ambient temperature (dry bulb) during this period must average 266 °K (-7 °C) ± 3 °K, and must:not be less than 260 °K (-13 °C) nor more than 272 °K (-1 °C),In addition, the temperature may:not fall below 263 °K (-10 °C) or exceed 269 °K (-4 °C),for more than three consecutive minutes. 4.3.4. If the vehicle is stabilized at 266 °K (-7 °C), in a separate area and is moved through a warm area to the test cell, the vehicle must be restabilized in the test cell for at least six times the period the vehicle is exposed to warmer temperatures. The ambient temperature (dry bulb) during this periodmust average 266 °K (-7 °C) ± 3 °K and must not be less than 260 °K (-13 °C) nor more than 272 °K (-1 °C).In addition, the temperature may:not fall below 263 °K (-10 °C) or exceed 269 °K (-4 °C), for more than three consecutive minutes. 5.DYNAMOMETER PROCEDURE 5.1.Summary 5.1.1. The emission sampling is performed over a test procedure consisting of the part one cycle (Annex III — Appendix 1 Figure III.1.1). Engine start-up, immediate sampling, operation over the part one cycle and engine shut-down make a complete low ambient temperature test, with a total test time of 780 seconds. The tailpipe emissions are diluted with ambient air and a continuously proportional sample is collected for analysis. The exhaust gases collected in the bag are analysed for hydrocarbons, carbon monoxide, and carbon dioxide. A parallel sample of the dilution air is similarly analysed for carbon monoxide, hydrocarbons and carbon dioxide. 5.2.Dynamometer operation 5.2.1.Cooling fan 5.2.1.1. A cooling fan is positioned so that cooling air is appropriately directed to the radiator (water cooling) or to the air intake (air-cooling) and to the vehicle. 5.2.1.2. For front-engined vehicles, the fan must be positioned in front of the vehicle, within 300 mm of it. In the case of rear-engined vehicles or if the above arrangement is impractical, the cooling fan must be positioned so that sufficient air is supplied to cool the vehicle. 5.2.1.3. The fan speed must be such that, within the operating range of 10 km/h to at least 50 km/h, the linear velocity of the air at the blower outlet is within ± 5 km/h of the corresponding roller speed. The final selection of the blower must have the following characteristics: area: at least 0,2 m2, height of the lower edge above ground: approximately 20 cm. As an alternative the blower speed must be at least 6 m/s (21,6 km/h). At the request of the manufacturer, for special vehicles (e. g. vans, off-road) the height of the cooling fan may be modified. 5.2.1.4. The vehicle speed as measured from the dynamometer roll(s) must be used (section 4.1.4.4 of Annex III). 5.2.3. Preliminary testing cycles may be carried out if necessary, to determine how best to actuate the accelerator and brake controls so as to achieve a cycle approximating to the theoretical cycle within the prescribed limits, or to permit sampling system adjustment. Such driving must be carried out before "START" according to Figure VII.1. 5.2.4. Humidity in the air must be kept low enough to prevent condensation on the dynamometer roll(s). 5.2.5. The dynamometer must be thoroughly warmed as recommended by the dynamometer manufacturer, and using procedures or control methods that assure stability of the residual frictional horsepower. 5.2.6. The time between dynamometer warming and the start of the emission test must be no longer than 10 minutes if the dynamometer bearings are not independently heated. If the dynamometer bearings are independently heated, the emission test must begin no longer than 20 minutes after dynamometer warming. 5.2.7. If the dynamometer horsepower must be adjusted manually, it must be set within one hour prior to the tailpipe emission test phase. The test vehicle may not be used to make the adjustment. The dynamometer, using automatic control of preselectable power settings, may be set at any time prior to the beginning of the emission test. 5.2.8. Before the emission test driving schedule may begin, the test cell temperature must be 266 °K (-7 °C) ± 2 °K, as measured in the air stream of the cooling fan with a maximum distance of 1 m-1,5 m from the vehicle. 5.2.9. During operation of the vehicle the heating and defrosting devices must be shut off. 5.2.10. The total driving distance or roller revolutions measured are recorded. 5.2.11. A four-wheel drive vehicle must be tested in a two-wheel drive mode of operation. The determination of the total road force for dynamometer setting is performed while operating the vehicle in its primary designed driving mode. 5.3.Performing the test 5.3.1. The provisions of sections 6.2 to 6.6, excluding 6.2.2, of Annex III apply in respect of starting the engine, carrying out the test and taking the emission samples. The sampling begins before or at the initiation of the engine start-up procedure and ends on conclusion of the final idling period of the last elementary cycle of the part one (urban driving cycle), after 780 seconds.The first driving cycle starts with a period of 11 seconds idling as soon as the engine has started. 5.3.2. For the analysis of the sampled emissions the provisions of section 7.2 of Annex III apply. In performing the exhaust sample analysis the technical service must exercise care to prevent condensation of water vapour in the exhaust gas sampling bags. 5.3.3. For the calculations of the mass emissions the provisions of section 8 of Annex III apply. 6.OTHER REQUIREMENTS 6.1.Irrational emission control strategy 6.1.1. Any irrational emission control strategy which results in a reduction in effectiveness of the emission control system under normal operating conditions at low temperature driving, so far as not covered by the standardized emission tests, may be considered a defeat device. ANNEX VIII Description of the ageing test for verifying the durability of anti-pollution devices 1.INTRODUCTION This Annex described the test for verifying the durability of anti-pollution devices equipping vehicles with positive-ignition or compression-ignition engines during an ageing test of 80000 km. 2.TEST VEHICLE 2.1. The vehicle must be in good mechanical order; the engine and the anti-pollution devices must be new.The vehicle may be the same as that presented for the type I test; this type I test has to be done after the vehicle has run at least 3000 km of the ageing cycle of section 5.1. 3.FUEL The durability test is conducted with a suitable commercially available fuel. 4.VEHICLE MAINTENANCE AND ADJUSTMENTS Maintenance, adjustments as well as the use of the test vehicle's controls shall be those recommended by the manufacturer. 5.VEHICLE OPERATION ON TRACK, ROAD OR ON CHASSIS DYNAMOMETER 5.1.Operating cycle During operation on track, road or on roller test bench, the distance must be covered according to the driving schedule (Figure VIII.5.1) described below: the durability test schedule is composed of 11 cycles covering 6 kilometres each, during the first nine cycles, the vehicle is stopped four times in the middle of the cycle, with the engine idling each time for 15 seconds, normal acceleration and deceleration, five decelerations in the middle of each cycle, dropping from cycle speed to 32 km/h, and the vehicle is gradually accelerated again until cycle speed is attained, the 10th cycle is carried out at a steady speed of 89 km/h, the 11th cycle begins with maximum acceleration from stop point up to 113 km/h. At half-way, braking is employed normally until the vehicle comes to a stop. This is followed by an idle period of 15 seconds and a second maximum acceleration. The schedule is then restarted from the beginning. The maximum speed of each cycle is given in the following Table.
Table VIII.5.1. Maximum speed of each cycle
Cycle Cycle speedin km/h
1 64
2 48
3 64
4 64
5 56
6 48
7 56
8 72
9 56
10 89
11 113
Figure VIII.5.1 Driving schedule01970L0220-20070101_en_img_21 5.1.1. At the request of the manufacturer, an alternative road test schedule may be used. Such alternative test schedules shall be approved by the technical service in advance of the test and must have substancially the same average speed, distribution of speeds, number of stops per kilometres and number of accelerations per kilometres as the driving schedule used on track or roller test bench, as detailed in 5.1 and Figure VIII.5.1. 5.1.2. The durability test, or if the manufacturer has chosen, the modified durability test shall be conducted until the vehicle has covered a minimum of 80000 km.
5.2.Test equipment 5.2.1.Chassis dynamometer 5.2.1.1. When the durability test is performed on a chassis dynamometer, the dynamometer must enable the cycle described in 5.1 to be carried out. In particular, it must be equipped with systems simulating inertia and resistance to progress. 5.2.1.2. The brake must be adjusted in order to absorb the power exerted on the driving wheels at a steady speed of 80 km/h. Methods to be applied to determine this power and to adjust the brake are the same as those described in Appendix 3 to Annex III. 5.2.1.3. The vehicle cooling system should enable the vehicle to operate at temperatures similar to those obtained on road (oil, water, exhaust system, etc.). 5.2.1.4. Certain other test bench adjustments and features are deemed to be identical, where necessary, to those described in Annex III of this Directive (inertia, for example, which may be mechanical or electronic). 5.2.1.5. The vehicle may be moved, where necessary, to a different bench in order to conduct emission measurement tests. 5.2.2.Operation on track or road When the durability test is completed on track or road, the vehicle's reference mass will be at least equal to that retained for tests conducted on a chassis dynamometer.
6.MEASURING EMISSIONS OF POLLUTANTS At the start of the test (0 km), and every 10000 km (± 400 km) or more frequently, at regular intervals until having covered 80000 km, tailpipe emissions are measured in accordance with the type I test as defined in section 5.3.1 of Annex I. The limit values to be complied with are those laid down in section 5.3.1.4 of Annex I. All exhaust emissions results must be plotted as a function of the running distance on the system rounded to the nearest kilometre and the best fit straight line fitted by the method of least squares shall be drawn through all these data points. This calculation shall not take into account the test results at 0 km.The data will be acceptable for use in the calculation of the deterioration factor only if the interpolated 6400 km and 80000 km points on this line are within the above mentioned limits. The data are still acceptable when a best fit straight line crosses an applicable limit with a negative slope (the 6400 km interpolated point is higher than the 80000 km interpolated point) but the 80000 km actual data point is below the limit.A multiplicative exhaust emission deterioration factor shall be calculated for each pollutant as follows: 01970L0220-20070101_en_img_22where: Mi1mass emission of the pollutant i in grams per km interpolated to 6400 km, Mi2mass emission of the pollutant i in grams per km interpolated to 80000 km. These interpolated values must be carried out to a minimum of four places to the right of the decimal point before dividing one by the other to determine the deterioration factor. The result must be rounded to three places to the right of the decimal point.If a deterioration factor is less than one, it is deemed to be equal to one.
ANNEX IX A.Specifications of reference fuels for testing vehicles to the emission limits given in row A of the table in section 5.3.1.4 of Annex I — Type I test 1.TECHNICAL DATA ON THE REFERENCE FUEL TO BE USED FOR TESTING VEHICLES EQUIPPED WITH POSITIVE-IGNITION ENGINES
Type: Unleaded petrol The values quoted in the specifications are "true values". In establishment of their limit values the terms of ISO 4259 Petroleum products — Determination and application of precision data in relation to methods of test have been applied and in fixing a minimum value, a minimum difference of 2R above zero has been taken into account; in fixing a maximum and minimum value, the minimum difference is 4R (R = reproducibility). Notwithstanding this measure, which is necessary for technical reasons, the manufacturer of fuels should nevertheless aim at a zero value where the stipulated maximum value is 2R and at the mean value in the case of quotations of maximum and minimum limits. Should it be necessary to clarify the questions as to whether a fuel meets the requirements of the specifications, the terms of ISO 4259 should be applied. The fuel may contain oxidation inhibitors and metal deactivators normally used to stabilise refinery gasoline streams, but detergent/dispersive additives and solvent oils must not be added. The actual sulphur content of the fuel used for the Type I test shall be reported.
Parameter Unit Limits Test method
Minimum Maximum
Research octane number, RON 95,0 EN 25164
Motor octane number, MON 85,0 EN 25163
Density at 15 °C kg/m3 748 762 ISO 3675
Reid vapour pressure kPa 56,0 60,0 EN 12
Distillation:
— initial boiling point °C 24 40 EN-ISO 3405
— evaporated at 100 °C % v/v 49,0 57,0 EN-ISO 3405
— evaporated at 150 °C % v/v 81,0 87,0 EN-ISO 3405
— final boiling point °C 190 215 EN-ISO 3405
Residue % v/v 2 EN-ISO 3405
Hydrocarbon analysis:
— olefins % v/v 10 ASTM D 1319
— aromatics % v/v 28,0 40,0 ASTM D 1319
— benzene % v/v 1,0 Pr. EN 12177
— saturates % v/v balance ASTM D 1319
Carbon/hydrogen ratio report report
Induction period minutes 480 EN-ISO 7536
Oxygen content % m/m 2,3 EN 1601
Existent gum mg/ml 0,04 EN-ISO 6246
Sulphur content mg/kg 100 Pr. EN ISO/DIS 14596
Class I copper corrosion 1 EN-ISO 2160
Lead content mg/l 5 EN 237
Phosphorus content mg/l 1,3 ASTM D 3231
2.TECHNICAL DATA ON THE REFERENCE FUEL TO BE USED FOR TESTING VEHICLES EQUIPPED WITH DIESEL ENGINE
Type: Diesel fuel The values quoted in the specifications are "true values". In establishment of their limit values the terms of ISO 4259 Petroleum products — Determination and application of precision data in relation to methods of test have been applied and in fixing a minimum value, a minimum difference of 2R above zero has been taken into account; in fixing a maximum and minimum value, the minimum difference is 4R (R = reproducibility). Notwithstanding this measure, which is necessary for technical reasons, the manufacturer of fuels should nevertheless aim at a zero value where the stipulated maximum value is 2R and at the mean value in the case of quotations of maximum and minimum limits. Should it be necessary to clarify the questions as to whether a fuel meets the requirements of the specifications, the terms of ISO 4259 should be applied. The range for cetane number is not in accordance with the requirements of a minimum range of 4R. However, in the case of a dispute between fuel supplier and fuel user, the terms of ISO 4259 may be used to resolve such disputes provided replicate measurements, of sufficient number to archive the necessary precision, are made in preference to single determinations. The actual sulphur content of the fuel used for the Type I test shall be reported. Even though oxidation stability is controlled, it is likely that shelf life will be limited. Advice should be sought from the supplier as to storage conditions and life.
Parameter Unit Limits Test method
Minimum Maximum
Cetane number 52,0 54,0 EN-ISO 5165
Density at 15 °C kg/m3 833 837 EN-ISO 3675
Distillation:
— 50 % point °C 245 EN-ISO 3405
— 95 % point °C 345 350 EN-ISO 3405
— final boiling point °C 370 EN-ISO 3405
Flash point °C 55 EN 22719
CFPP °C 5 EN 116
Viscosity at 40 °C mm2/s 2,5 3,5 EN-ISO 3104
Polycyclic aromatic hydrocarbons % m/m 3 6,0 IP 391
Sulphur content mg/kg 300 Pr. EN-ISO/DIS 14596
Copper corrosion 1 EN-ISO 2160
Conradson carbon residue (10 % DR) % m/m 0,2 EN-ISO 10370
Ash content % m/m 0,01 EN-ISO 6245
Water content % m/m 0,02 EN-ISO 12937
Neutralisation (strong acid) number mg KOH/g 0,02 ASTM D 974-95
Oxidation stability mg/ml 0,025 EN-ISO 12205
New and better method for polycyclic aromatics under development % m/m EN 12916
B.Specifications of reference fuels for testing vehicles to the emission limits given in row B of the table in section 5.3.1.4 of Annex I — Type I test 1.TECHNICAL DATA ON THE REFERENCE FUEL TO BE USED FOR TESTING VEHICLES EQUIPPED WITH POSITIVE-IGNITION ENGINES
Type: Unleaded petrol The values quoted in the specifications are "true values". In establishment of their limit values the terms of ISO 4259 Petroleum products — Determination and application of precision data in relation to methods of test have been applied and in fixing a minimum value, a minimum difference of 2R above zero has been taken into account; in fixing a maximum and minimum value, the minimum difference is 4R (R = reproducibility). Notwithstanding this measure, which is necessary for technical reasons, the manufacturer of fuels should nevertheless aim at a zero value where the stipulated maximum value is 2R and at the mean value in the case of quotations of maximum and minimum limits. Should it be necessary to clarify the questions as to whether a fuel meets the requirements of the specifications, the terms of ISO 4259 should be applied. The fuel may contain oxidation inhibitors and metal deactivators normally used to stabilise refinery gasoline streams, but detergent/dispersive additives and solvent oils must not be added. The actual sulphur content of the fuel used for the Type I test shall be reported.
Parameter Unit Limits Test method
Minimum Maximum
Research octane number, RON 95,0 EN 25164
Motor octane number, MON 85,0 EN 25163
Density at 15 °C kg/m3 740 754 ISO 3675
Reid vapour pressure kPa 56,0 60,0 PrEN ISO 13016-1 (DVPE)
Distillation:
— evaporated at 70 °C % v/v 24,0 40,0 EN-ISO 3405
— evaporated at 100 °C % v/v 50,0 58,0 EN-ISO 3405
— evaporated at 150 °C % v/v 83,0 89,0 EN-ISO 3405
— final boiling point °C 190 210 EN-ISO 3405
Residue % v/v 2,0 EN-ISO 3405
Hydrocarbon analysis:
— olefins % v/v 10,0 ASTM D 1319
— aromatics % v/v 29,0 35,0 ASTM D 1319
— benzene % v/v 1,0 ASTM D 1319
— saturates % v/v report Pr. EN 12177
Carbon/hydrogen ratio report
Induction period minutes 480 EN-ISO 7536
Oxygen content % m/m 1,0 EN 1601
Existent gum mg/ml 0,04 EN-ISO 6246
Sulphur content mg/kg 10 ASTM D 5453
Copper corrosion class 1 EN-ISO 2160
Lead content mg/l 5 EN 237
Phosphorus content mg/l 1,3 ASTM D 3231
2.TECHNICAL DATA ON THE REFERENCE FUEL TO BE USED FOR TESTING VEHICLES EQUIPPED WITH DIESEL ENGINE
Type: Diesel fuel The values quoted in the specifications are "true values". In establishment of their limit values the terms of ISO 4259 Petroleum products — Determination and application of precision data in relation to methods of test have been applied and in fixing a minimum value, a minimum difference of 2R above zero has been taken into account; in fixing a maximum and minimum value, the minimum difference is 4R (R = reproducibility). Notwithstanding this measure, which is necessary for technical reasons, the manufacturer of fuels should nevertheless aim at a zero value where the stipulated maximum value is 2R and at the mean value in the case of quotations of maximum and minimum limits. Should it be necessary to clarify the questions as to whether a fuel meets the requirements of the specifications, the terms of ISO 4259 should be applied. The range for cetane number is not in accordance with the requirements of a minimum range of 4R. However, in the case of a dispute between fuel supplier and fuel user, the terms of ISO 4259 may be used to resolve such disputes provided replicate measurements, of sufficient number to archive the necessary precision, are made in preference to single determinations. The actual sulphur content of the fuel used for the Type I test shall be reported. Even though oxidation stability is controlled, it is likely that shelf life will be limited. Advice should be sought from the supplier as to storage conditions and life.
Parameter Unit Limits Test method
Minimum Maximum
Cetane number 52,0 54,0 EN-ISO 5165
Density at 15 °C kg/m3 833 837 EN-ISO 3675
Distillation:
— 50 % point °C 245 EN-ISO 3405
— 95 % point °C 345 350 EN-ISO 3405
— final boiling point °C 370 EN-ISO 3405
Flash point °C 55 EN 22719
CFPP °C 5 EN 116
Viscosity at 40 °C mm2/s 2,3 3,3 EN-ISO 3104
Polycyclic aromatic hydrocarbons % m/m 3,0 6,0 IP 391
Sulphur content mg/kg 10 ASTM D 5453
Copper corrosion Class 1 EN-ISO 2160
Conradson carbon residue (10 % DR) % m/m 0,2 EN-ISO 10370
Ash content % m/m 0,01 EN-ISO 6245
Water content % m/m 0,02 EN-ISO 12937
Neutralisation (strong acid) number mg KOH/g 0,02 ASTM D 974
Oxidation stability mg/ml 0,025 EN-ISO 12205
Lubricity (HFRR wear scan diameter at 60 °C) μm 400 CEC F-06-A-96
FAME Prohibited
C.Specifications of reference fuel to be used for testing vehicles equipped with positive-ignition engines at low ambient temperature — Type VI test
Type: Unleaded petrol The values quoted in the specifications are "true values". In establishment of their limit values the terms of ISO 4259 Petroleum products — Determination and application of precision data in relation to methods of test have been applied and in fixing a minimum value, a minimum difference of 2R above zero has been taken into account; in fixing a maximum and minimum value, the minimum difference is 4R (R = reproducibility). Notwithstanding this measure, which is necessary for technical reasons, the manufacturer of fuels should nevertheless aim at a zero value where the stipulated maximum value is 2R and at the mean value in the case of quotations of maximum and minimum limits. Should it be necessary to clarify the questions as to whether a fuel meets the requirements of the specifications, the terms of ISO 4259 should be applied. The fuel may contain oxidation inhibitors and metal deactivators normally used to stabilise refinery gasoline streams, but detergent/dispersive additives and solvent oils must not be added. The actual sulphur content of the fuel used for the Type VI test shall be reported.
Parameter Unit Limits Test method
Minimum Maximum
Research octane number, RON 95,0 EN 25164
Motor octane number, MON 85,0 EN 25163
Density at 15 °C kg/m3 740 754 ISO 3675
Reid vapour pressure kPa 56,0 95,0 Pr. EN ISO 13016-1 (DVPE)
Distillation:
— evaporated at 70 °C % v/v 24,0 40,0 EN-ISO 3405
— evaporated at 100 °C % v/v 50,0 58,0 EN-ISO 3405
— evaporated at 150 °C % v/v 83,0 89,0 EN-ISO 3405
— final boiling point °C 190 210 EN-ISO 3405
Residue % v/v 2,0 EN-ISO 3405
Hydrocarbon analysis:
— olefins % v/v 10,0 ASTM D 1319
— aromatics % v/v 29,0 35,0 ASTM D 1319
— benzene % v/v 1,0 ASTM D 1319
— saturates % v/v report Pr. EN 12177
Carbon/hydrogen ratio report
Induction period minutes 480 EN-ISO 7536
Oxygen content % m/m 1,0 EN 1601
Existent gum mg/ml 0,04 EN-ISO 6246
Sulphur content mg/kg 10 ASTM D 5453
Copper corrosion Class 1 EN-ISO 2160
Lead content mg/l 5 EN 237
Phosphorus content mg/l 1,3 ASTM D 3231
ANNEX IXa SPECIFICATIONS OF GASEOUS REFERENCE FUELS A.Technical data of the LPG reference fuels 1.TECHNICAL DATA OF THE LPG REFERENCE FUELS USED FOR TESTING VEHICLES TO THE EMISSION LIMITS GIVEN IN ROW A OF THE TABLE IN SECTION 5.3.1.4 OF ANNEX I — TYPE I TEST
This method may not accurately determine the presence of corrosive materials if the sample contains corrosion inhibitors or other chemicals which diminish the corrosivity of the sample to the copper strip. Therefore, the addition of such compounds for the sole purpose of biasing the test method is prohibited.
Parameter Unit Fuel A Fuel B Test method
Composition: ISO 7941
C3-content % vol. 30 ± 2 85 ± 2
C4-content % vol. balance balance
< C3 , > C4 % vol. maximum 2 maximum 2
Olefins % vol. maximum 12 maximum 15
Evaporation residue mg/kg maximum 50 maximum 50 ISO 13757
Water at 0 °C free free visual inspection
Total sulphur content mg/kg maximum 50 maximum 50 EN 24260
Hydrogen sulphide none none ISO 8819
Copper strip corrosion rating class 1 class 1 ISO 6251
Odour characteristic characteristic
Motor octane number minimum 89 minimum 89 EN 589 Annex B
2.TECHNICAL DATA OF THE LPG REFERENCE FUELS USED FOR TESTING VEHICLES TO THE EMISSION LIMITS GIVEN IN ROW B OF THE TABLE IN SECTION 5.3.1.4 OF ANNEX I — TYPE I TEST
This method may not accurately determine the presence of corrosive materials if the sample contains corrosion inhibitors or other chemicals which diminish the corrosivity of the sample to the copper strip. Therefore, the addition of such compounds for the sole purpose of biasing the test method is prohibited.
Parameter Unit Fuel A Fuel B Test method
Composition: ISO 7941
C3-content % vol 30 ± 2 85 ± 2
C4-content % vol balance balance
< C3 , > C4 % vol maximum 2 maximum 2
Olefins % vol maximum 12 maximum 15
Evaporation residue mg/kg maximum 50 maximum 50 ISO 13757
Water at 0 °C free free Visual inspection
Total sulphur content mg/kg maximum 10 maximum 10 EN 24260
Hydrogen sulphide none none ISO 8819
Copper strip corrosion Rating class 1 class 1 ISO 6251
Odour characteristic characteristic
Motor octane number minimum 89 minimum 89 EN 589 Annex B
B.Technical data of the ng reference fuels
Inerts (different from N2) + C2 +C2+. Value to be determined at 293,2 K (20 °C) and 101,3 kPa. Value to be determined at 273,2 K (0 °C) and 101,3 kPa.Reference fuel G20 Composition: Reference fuel G25 Composition:
Characteristics Units Basis Limits Test method
minimum maximum
Methane % mole 100 99 100 ISO 6974
Balance % mole 1 ISO 6974
N2 % mole ISO 6974
Sulphur content mg/m3 10 ISO 6326-5
Wobbe Index (net) MJ/m3 48,2 47,2 49,2
Methane % mole 86 84 88 ISO 6974
Balance % mole 1 ISO 6974
N2 % mole 14 12 16 ISO 6974
Sulphur content mg/m3 10 ISO 6326-5
Wobbe Index (net) MJ/m3 39,4 38,2 40,6
ANNEX X MODEL(Maximum format: A4 (210 × 297 mm)) EC TYPE-APPROVAL CERTIFICATE 01970L0220-20070101_en_img_23 ANNEX XI ON-BOARD DIAGNOSTICS (OBD) FOR MOTOR VEHICLES 1.INTRODUTION This Annex applies to the functional aspects of on-board diagnostic (OBD) system for the emission control of motor vehicles. 2.DEFINITIONS For the purposes of this Annex: 2.1. "OBD" means an on-board diagnostic system for emission control which must have the capability of identifying the likely area of malfunction by means of fault codes stored in computer memory. 2.2. "Vehicle type" means a category of power-driven vehicles which do not differ in such essential engine and OBD system characteristics as defined in Appendix 2. 2.3. "Vehicle family" means a manufacturer's grouping of vehicles which, through their design, are expected to have similar exhaust emission and OBD system characteristics. Each engine of this family must have complied with the requirements of this Directive. 2.4. "Emission control system" means the electronic engine management controller and any emission-related component in the exhaust or evaporative system which supplies an input to or receives an output from this controller. 2.5. "Malfunction indicator (MI)" means a visible or audible indicator that clearly informs the driver of the vehicle in the event of a malfunction of any emission-related component connected to the OBD system, or the OBD system itself. 2.6. "Malfunction" means the failure of an emission-related component or system that would result in emissions exceeding the limits in section 3.3.2 or if the OBD system is unable to fulfil the basic monitoring requirements of this Annex. 2.7. "Secondary air" refers to air introduced into the exhaust system by means of a pump or aspirator valve or other means that is intended to aid in the oxidation of HC and CO contained in the exhaust gas stream. 2.8. "Engine misfire" means lack of combustion in the cylinder of a positive-ignition engine due to absence of spark, poor fuel metering, poor compression or any other cause. In terms of OBD monitoring it is that percentage of misfires out of a total number of firing events (as declared by the manufacturer) that would result in emissions exceeding the limits given in section 3.3.2 or. that percentage that could lead to an exhaust catalyst, or catalysts, overheating causing irreversible damage. 2.9. "Type I test" means the driving cycle (Parts One and Two) used for emission approvals, as detailed in Annex III, Appendix 1. 2.10. "A driving cycle" consists of engine start-up, driving mode where a malfunction would be detected if present, and engine shut-off. 2.11. "A warm-up cycle" means sufficient vehicle operation such that the coolant temperature has risen by a least 22 °K from engine starting and reaches a minimum temperature of 343 °K (70 °C). 2.12. "Fuel trim" refers to feedback adjustments to the base fuel schedule. Short-term fuel trim refers to dynamic or instantaneous adjustments. Long-term fuel trim refers to much more gradual adjustments to the fuel calibration schedule than short-term trim adjustments. These long-term adjustments compensate for vehicle differences and gradual changes that occur over time. 2.13. "Calculated load value" refers to an indication of the current airflow divided by peak airflow, where peak airflow is corrected for altitude, if available. This definition provides a dimensionless number that is not engine specific and provides the service technician with an indication of the proportion of engine capacity that is being used (with wide open throttle as 100 %); 01970L0220-20070101_en_img_24 2.14. "Permanent emission default mode" refers to a case where the engine management controller permanently switches to a setting that does not require an input from a failed component or system where such a failed component or system would result in an increase in emissions from the vehicle to a level above the limits given in section 3.3.2. 2.15. "Power take-off unit" means an engine-driven output provision for the purposes of powering auxiliary, vehicle mounted, equipment. 2.16. "Access" means the availability of all emission-related OBD data including all fault codes required for the inspection, diagnosis, servicing or repair of emissions-related parts of the vehicle, via the serial interface for the standard diagnostic connection (pursuant to Appendix 1, section 6.5.3.5 of this Annex). 2.17. "Unrestricted" means access not dependent on an access code obtainable only from the manufacturer, or a similar device, or access allowing evaluation of the data produced without the need for any unique decoding information, unless that information itself is standardised. 2.18. "Standardised" means that all data stream information, including all fault codes used, shall be produced only in accordance with industry standards which, by virtue of the fact that their format and their permitted options are clearly defined, provide for a maximum level of harmonisation in the motor vehicle industry, and whose use is expressly permitted in this Directive. 2.19. "Repair information" means all information required for diagnosis, servicing, inspection, periodic monitoring or repair of the vehicle and which the manufacturers provide for their authorised dealers/repair shops. Where necessary, such information shall include service handbooks, technical manuals, diagnosis information (e.g. minimum and maximum theoretical values for measurements), wiring diagrams, the software calibration identification number applicable to a vehicle type, instructions for individual and special cases, information provided concerning tools and equipment, data record information and two-directional monitoring and test data. The manufacturer shall not be obliged to make available that information which is covered by intellectual property rights or constitutes specific know-how of manufacturers and/or OEM suppliers; in this case the necessary technical information shall not be improperly withheld. 2.20. "Deficiency" means, in respect of vehicle OBD systems, that up to two separate components or systems that are monitored contain temporary or permanent operating characteristics that impair the otherwise efficient OBD monitoring of those components or systems or do not meet all of the other detailed requirements for OBD. Vehicles may be type-approved, registered and sold with such deficiencies according to the requirements of Section 4 of this Annex. 3.REQUIREMENTS AND TESTS 3.1. All vehicles must be equipped with an OBD system so designed, constructed and installed in a vehicle as to enable it to identify types of deterioration or malfunction over the entire life of the vehicle. In achieving this objective the approval authority must accept that vehicles which have travelled distances in excess of the Type V durability distance, referred to in 3.3.1, may show some deterioration in OBD system performance such that the emission limits given in 3.3.2 may be exceeded before the OBD system signals a failure to the driver of the vehicle. 3.1.1. Access to the OBD system required for the inspection, diagnosis, servicing or repair of the vehicle must be unrestricted and standardised. All emission-related fault codes must be consistent with Section 6.5.3.4 of Appendix 1 to this Annex. 3.1.2. No later than three months after the manufacturer has provided any authorised dealer or repair shop within the Community with repair information, the manufacturer shall make that information (including all subsequent amendments and supplements) available upon reasonable and non-discriminatory payment and shall notify the approval authority accordingly.In the event of failure to comply with these provisions the approval authority shall take appropriate measures to ensure that repair information is available, in accordance with the procedures laid down for type-approval and in-service surveys. 3.2. The OBD system must be so designed, constructed and installed in a vehicle as to enable it to comply with the requirements of this Annex during conditions of normal use. 3.2.1.Temporary disablement of the OBD system 3.2.1.1. A manufacturer may disable the OBD system if its ability to monitor is affected by low fuel levels. Disablement must not occur when the fuel tank level is above 20 % of the nominal capacity of the fuel tank. 3.2.1.2. A manufacturer may disable the OBD system at ambient engine starting temperatures below 266 °K (-7 °C) or at elevations over 2500 metres above sea level provided the manufacturer submits data and/or an engineering evaluation which adequately demonstrate that monitoring would be unreliable when such conditions exist. A manufacturer may also request disablement of the OBD system at other ambient engine starting temperatures if he demonstrates to the authority with data and/or an engineering evaluation that misdiagnosis would occur under such conditions. 3.2.1.3. For vehicles designed to accommodate the installation of power take-off units, disablement of affected monitoring systems is permitted provided disablement occurs only when the power take-off unit is active. 3.2.2.Engine misfire — vehicles equipped with positive-ignition engines 3.2.2.1. Manufacturers may adopt higher misfire percentage malfunction criteria than those declared to the authority, under specific engine speed and load conditions where it can be demonstrated to the authority that the detection of lower levels of misfire would be unreliable. 3.2.2.2. When a manufacturer can demonstrate to the authority that the detection of higher levels of misfire percentages is still not feasible, or that misfire cannot be distinguished from other effects (e.g. rough roads, transmission shifts, after engine starting; etc.) the misfire monitoring system may be disabled when such conditions exist. 3.3.Description of tests 3.3.1. The test are carried out on the vehicle used for the Type V durability test, given in Annex VIII, and using the test procedure in Appendix I to this Annex. Tests are carried out at the conclusion of the Type V durability testing. When no Type V durability testing is carried out, or at the request of the manufacturer, a suitably aged and representative vehicle may be used for these OBD demonstration tests. 3.3.2. The OBD system must indicate the failure of an emission-related component or system when that failure results in emissions exceeding the threshold limits given below:
For compression ignition engines. Except vehicles the maximum mass of which exceeds 2500 kg. And those category M vehicles which are specified in note 2. The Commission proposal referred to in Article 3(1) of this Directive shall contain the threshold limit values for OBD for 2005/6 for M1 and N1 vehicles.
Reference mass(RW)(kg) Mass of carbon monoxide Mass of total hydrocarbons Mass of oxides of nitrogen Mass of particulates
Category Class (CO)L1(g/km) (THC)L2(g/km) (NOx)L3(g/km) (PM)L4(g/km)
Petrol Diesel Petrol Diesel Petrol Diesel Diesel
M all 3,20 3,20 0,40 0,40 0,60 1,20 0,18
N1 I RW ≤ 1305 3,20 3,20 0,40 0,40 0,60 1,20 0,18
II 1305 < RW ≤ 1760 5,80 4,00 0,50 0,50 0,70 1,60 0,23
III 1760 < RW 7,30 4,80 0,60 0,60 0,80 1,90 0,28
3.3.3.Monitoring requirements for vehicles equipped with positive-ignition engines In satisfying the requirements of 3.3.2 the OBD system must, at a minimum, monitor for: 3.3.3.1. reduction in the efficiency of the catalytic converter with respect to the emissions of HC only. Manufacturers may monitor the front catalyst alone or in combination with the next catalyst(s) downstream. Each monitored catalyst or catalyst combination shall be considered malfunctioning when the emissions exceed the HC threshold given in the table in Section 3.3.2; 3.3.3.2. the presence of engine misfire in the engine operating region bounded by the following lines: (a)a maximum speed of 4500min-1 or 1000 min-1 greater than the highest speed occurring during a Type I test cycle, whichever is the lower; (b)the positive torque line (i. e. engine load with the transmission in neutral); (c)a line joining the following engine operating points: the positive torque line at 3000 min-1 and a point on the maximum speed line defined in (a) above with the engine's manifold vacuum at 13,33 kPa lower than that at the positive torque line. 3.3.3.3. oxygen sensor deterioration 3.3.3.4. if active on the selected fuel, other emission control system components or systems, or emission-related powertrain components or systems which are connected to a computer, the failure of which may result in tailpipe emissions exceeding the limits given in 3.3.2; 3.3.3.5. unless otherwise monitored, any other emission-related powertrain component connected to a computer, including any relevant sensors to enable monitoring functions to be carried out, must be monitored for circuit continuity; 3.3.3.6. the electronic evaporative emission purge control must, at a minimum, be monitored for circuit continuity. 3.3.4.Monitoring requirements for vehicles equipped with compression-ignition engines In satisfying the requirements of 3.3.2 the OBD system must monitor: 3.3.4.1. Where fitted, reduction in the efficiency of the catalytic converter; 3.3.4.2. Where fitted, the functionality and integrity of the particulate trap; 3.3.4.3. The fuel-injection system electronic fuel quantity and timing actuator(s) is/are monitored for circuit continuity and total functional failure; 3.3.4.4. Other emission control system components or systems, or emission-related powertrain components or systems, which are connected to a computer, the failure of which may result in tailpipe emissions exceeding the limits given in 3.3.2. Examples of such systems or components are those for monitoring and control of air mass-flow, air volumetric flow (and temperature), boost pressure and inlet manifold pressure (and relevant sensors to enable these functions to be carried out). 3.3.4.5. Unless otherwise monitored, any other emission-related powertrain component connected to a computer must be monitored for circuit continuity. 3.3.5. Manufacturers may demonstrate to the approval authority that certain components or systems need not be monitored if, in the event of their total failure or removal, emissions do not exceed the emission limits given in 3.3.2.
3.4. A sequence of diagnostic checks must be initiated at each engine start and completed at least once provided that the correct test conditions are met. The test conditions must be selected in such a way that they all occur under normal driving as represented by the Type I test. 3.5.Activation of malfunction indicator (MI) 3.5.1. The OBD system must incorporate a malfunction indicator readily perceivable to the vehicle operator. The MI must not be used for any other purpose except to indicate emergency start-up or limp-home routines to the driver. The MI must be visible in all reasonable lighting conditions. When activated, it must display a symbol in conformity with ISO 2575International Standard ISO 2575-1982 (E), entitled "Road vehicles — Symbols for controls indicators and tell-tales", Symbol Number 4.36.. A vehicle must not be equipped with more than one general purpose MI for emission-related problems. Separate specific purpose telltales (e. g. brake system, fasten seat belt, oil pressure, etc.) are permitted. The use of red for an MI is prohibited. 3.5.2. For strategies requiring more than two preconditioning cycles for MI activation, the manufacturer must provide data and/or an engineering evaluation which adequately demonstrates that the monitoring system is equally effective and timely in detecting component deterioration. Strategies requiring on average more than 10 driving cycles for MI activation are not accepted. The MI must also activate whenever the engine control enters a permanent emission default mode of operation if the emission limits given in 3.3.2 are exceeded or if the OBD system is unable to fulfil the basic monitoring requirements specified in section 3.3.3 or section 3.3.4 of this Annex. The MI must operate in a distinct warning mode, e.g. a flashing light, under any period during which engine misfire occurs at a level likely to cause catalyst damage, as specified by the manufacturer. The MI must also activate when the vehicle's ignition is in the "key-on" position before engine starting or cranking and de-activate after engine starting if no malfunction has previously been detected. 3.6.Fault code storage The OBD system must record fault code(s) indicating the status of the emission control system. Separate status codes must be used to identify correctly functioning emission control systems and those emission control systems which need further vehicle operation to be fully evaluated. If the MI is activated due to deterioration or malfunction or permanent emission default modes of operation, a fault code must be stored that identifies the type of malfunction. A fault code must also be stored in the cases referred to in sections 3.3.3.5 and 3.3.4.5 of this Annex. 3.6.1. The distance travelled by the vehicle while the MI is activated must be available at any instant through the serial port on the standard link connectorThis requirement is only applicable from 1 January 2003 to new types of vehicles with an electronic speed input to the engine management. It applies to all new types of vehicles entering into service from 1 January 2005.. 3.6.2. In the case of vehicles equipped with positive-ignition engines, misfiring cylinders need not be uniquely identified if a distinct single or multiple cylinder misfire fault code is stored. 3.7.Extinguishing the MI 3.7.1. If misfire at levels likely to cause catalyst damage (as specified by the manufacturer) is not present any more, or if the engine is operated after changes to speed and load conditions where the level of misfire will not cause catalyst damage, the MI may be switched back to the previous state of activation during the first driving cycle on which the misfire level was detected and may be switched to the normal activated mode on subsequent driving cycles. If the MI is switched back to the previous state of activation, the corresponding fault codes and stored freeze-frame conditions may be erased. 3.7.2. For all other malfunctions, the MI may be de-activated after three subsequent sequential driving cycles during which the monitoring system responsible for activating the MI ceases to detect the malfunction and if no other malfunction has been identified that would independently activate the MI. 3.8.Erasing a fault code 3.8.1. The OBD system may erase a fault code and the distance travelled and freeze-frame information if the same fault is not re-registered in at least 40 engine warm-up cycles. 3.9.Bi-fuelled gas vehicles 3.9.1. For bi-fuelled gas vehicles, the procedures: activation of malfunction indicator (MI) (see section 3.5 of this Annex), fault code storage (see section 3.6 of this Annex), extinguishing the MI (see section 3.7 of this Annex), erasing a fault code (see section 3.8 of this Annex), shall be executed independently of each other when the vehicle is operated on petrol or on gas. When the vehicle is operated on petrol, the result of any of the procedures indicated above shall not be affected when the vehicle is operated on gas. When the vehicle is operated on gas, the result of any of the procedures indicated above shall not be affected when the vehicle is operated on petrol.Notwithstanding this requirement, the status code (described in section 3.6 of this Annex) shall indicate fully evaluated control systems for both fuel types (petrol and gas) when the control systems are fully evaluated for one of the fuel types.
4.REQUIREMENTS RELATING TO THE TYPE-APPROVAL OF ON-BOARD DIAGNOSTIC SYSTEMS 4.1. A manufacturer may request to the authority that an OBD system be accepted for type-approval even though the system contains one or more deficiencies such that the specific requirements of this Annex are not fully met. 4.2. In considering the request, the authority shall determine whether compliance with the requirements of this Annex is infeasible or unreasonable.The authority shall take into consideration data from the manufacturer that details such factors as, but not limited to, technical feasibility, lead time and production cycles including phase-in or phase-out of engines or vehicle designs and programmed upgrades of computers, the extent to which the resultant OBD system will be effective in complying with the requirements of this directive and that the manufacturer has demonstrated an acceptable level of effort toward compliance with the requirements of this Directive. 4.2.1. The authority will not accept any deficiency request that includes the complete lack of a required diagnostic monitor. 4.2.2. The authority will not accept any deficiency request that does not respect the OBD threshold limits in Section 3.3.2. 4.3. In determining the identified order of deficiencies, deficiencies relating to sections 3.3.3.1, 3.3.3.2 and 3.3.3.3 of this Annex for positive-ignition engines and sections 3.3.4.1, 3.3.4.2 and 3.3.4.3 of this Annex for compression-ignition engines shall be identified first. 4.4. Prior to or at the time of type-approval, no deficiency shall be granted in respect of the requirements of section 6.5, except section 6.5.3.4 of Appendix 1 to this Annex. This section does not apply to bi-fuelled gas vehicles. 4.5.Bi-fuelled gas vehicles 4.5.1. Notwithstanding the requirements of section 3.9.1, and where requested by the manufacturer, the type-approval authority shall accept the following deficiencies as meeting the requirements of this Annex for the purpose of the type-approval of bi-fuelled gas vehicles: erasing of fault codes, distance travelled and freeze-frame information after 40 engine warm-up cycles, independent of the fuel currently in use, activation of the MI on both fuel types (petrol and gas) after the detection of a malfunction on one of the fuel types, de-activation of the MI after three subsequent sequential driving cycles without malfunction, independent of the fuel currently in use, use of two status codes, one for each fuel type. Further options may be requested by the manufacturer and granted at the discretion of the type-approval authority. 4.5.2. Notwithstanding the requirements of section 6.6 of Appendix 1 to this Annex, and where requested by the manufacturer, the type-approval authority shall accept the following deficiencies as meeting the requirements of this Annex for the evaluation and transmission of diagnostic signals: transmission of the diagnostic signals for the fuel currently in use on a single source address, evaluation of one set of diagnostic signals for both fuel types (corresponding to the evaluation on mono-fuelled gas vehicles, and independent of the fuel currently in use), selection of one set of diagnostic signals (associated to one of the two fuel types) by the position of a fuel switch, evaluation and transmission of one set of diagnostic signals for both fuels in the petrol computer independent of the fuel in use. The gas supply system computer will evaluate and transmit the gaseous fuel system related diagnostic signals and store fuel status history. Further options may be requested by the manufacturer and granted at the discretion of the type-approval authority. 4.6.Deficiency period 4.6.1. A deficiency may be carried-over for a period of two years after the date of type-approval of the vehicle type unless it can be adequately demonstrated that substantial vehicle hardware modifications and additional lead-time beyond two years would be necessary to correct the deficiency. In such a case, the deficiency may be carried-over for a period not exceeding three years. 4.6.1.1. In the case of a bi-fuelled gas vehicle, a deficiency granted in accordance with section 4.5 may be carried-over for a period of three years after the date of type-approval of the vehicle type unless it can be adequately demonstrated that substantial vehicle hardware modifications and additional lead-time beyond three years would be necessary to correct the deficiency. In such a case, the deficiency may be carried-over for a period not exceeding four years. 4.6.2. A manufacturer may request that the type-approval authority grant a deficiency retrospectively when such a deficiency is discovered after the original type-approval. In this case, the deficiency may be carried-over for a period of two years after the date of notification ton the type-approval authority unless it can be adequately demonstrated that substantial vehicle hardware modifications and additional lead-time beyond two years would be necessary to correct the deficiency. In such a case, the deficiency may be carried-over for a period not exceeding three years. 4.7. The authority shall notify its decision in granting a deficiency request to all authorities in other Member States according to the requirements of Article 4 to Directive 70/156/EEC. 5.ACCESS TO OBD INFORMATION 5.1. Applications for type-approval or amendment of a type-approval according to either Article 3 or Article 5 of Directive 70/156/EEC shall be accompanied by the relevant information concerning the vehicle OBD system. This relevant information shall enable manufacturers of replacement or retrofit components to make the parts they manufacture compatible with the vehicle OBD system with a view to fault-free operation assuring the vehicle user against malfunctions. Similarly, such relevant information shall enable the manufacturers of diagnostic tools and test equipment to make tools and equipment that provide for effective and accurate diagnosis of vehicle emission control systems. 5.2. Upon request, the type-approval authorities shall make Appendix 2 to the EC type-approval certificate containing the relevant information on the OBD system available to any interested components, diagnostic tools or test equipment manufacturer on a non-discriminatory basis. 5.2.1. If a type-approval authority receives a request from any interested components, diagnostic tools or test equipment manufacturer for information on the OBD system of a vehicle that has been type-approved to a previous version of Directive 70/220/EEC, the type-approval authority shall, within 30 days, request the manufacturer of the vehicle in question to make available the information required in section 3.2.12.2.8.6 of Annex II. The requirement of the second paragraph of section 3.2.12.2.8.6 is not applicable, the manufacturer shall submit this information to the type-approval authority within two months of the request, the type-approval authority shall transmit this information to the approval authorities of the Member States and the authority which granted the original type-approval shall attach this information to Annex II to the vehicle type-approval information. This requirement shall not invalidate any approval previously granted pursuant to Directive 70/220/EEC nor prevent extensions to such approvals under the terms of the Directive under which they were originally granted. 5.2.2. Information can only be requested for replacement or service components that are subject to EC type-approval, or for components that form part of a system that is subject to EC type-approval. 5.2.3. The request for information must identify the exact specification of the vehicle model for which the information is required. It must confirm that the information is required for the development of replacement or retrofit parts or components or diagnostic tools or test equipment.
ANNEX XII EC TYPE-APPROVAL FOR A VEHICLE FUELLED BY LPG OR NATURAL GAS WITH REGARD TO ITS EMISSIONS 1.INTRODUCTION This Annex describes the special requirements that apply in the case of an approval of a vehicle that runs on LPG or natural gas, or that can run either on unleaded petrol or LPG or natural gas, in so far as the testing on LPG or natural gas is concerned.In the case of LPG and natural gas there is on the market a large variation in fuel composition, requiring the fuelling system to adapt its fuelling rates to these compositions. To demonstrate this capability, the vehicle has to be tested in the test type I on two extreme reference fuels and demonstrate the self-adaptability of the fuelling system. Whenever the self adaptability of a fuelling system has been demonstrated on a vehicle, such a vehicle may be considered as a parent of a family. Vehicles that comply with the requirements of members of that family, if fitted with the same fuelling system, need to be tested on only one fuel. 2.DEFINITIONS For the purpose of this Annex: 2.1. A parent vehicle means a vehicle that is selected to act as the vehicle on which the self adaptability of a fuelling system is going to be demonstrated, and to which the members of a family refer. It is possible to have more than one parent vehicle in a family. 2.2. A member of the family is a vehicle that shares the following essential characteristics with its parent(s): 2.2.1. (a)It is produced by the same vehicle manufacturer. (b)It is subject to the same emission limits. (c)If the gas fuelling system has a central metering for the whole engine: It has a certified power output between 0,7 and 1,15 times that of the engine of the parent vehicle.If the gas fuelling system has an individual metering per cylinder:It has a certified power output per cylinder between 0,7 and 1,15 times that of the engine of the parent vehicle. (d)If fitted with a catalyst system, it has the same type of catalyst i.e. three-way, oxidation, de NOx. (e)It has a gas fuelling system (including the pressure regulator) from the same system manufacturer and of the same type: induction, vapour injection (single point, multipoint), liquid injection (single point, multipoint). (f)This gas fuelling system is controlled by an ECU of the same type and technical specification, containing the same software principles and control strategy. 2.2.2. With regard to requirement (c): in the case where a demonstration shows two gas fuelled vehicles could be members of the same family with the exception of their certified power output, respectively P1 and P2 (P1 < P2), and both are tested as if they were parent vehicles, the family relation will be considered valid for any vehicle with a certified power output between 0,7 * P1 and 1,15 * P2. 3.GRANTING OF AN EC TYPE-APPROVAL EC type-approval is granted subject to the following requirements: 3.1. Exhaust emissions approval of a parent vehicle:The parent vehicle should demonstrate its capability to adapt to any fuel composition that may occur across the market. In the case of LPG there are variations in C3/C4 composition. In the case of natural gas there are generally two types of fuel, high calorific fuel (H-gas) and low calorific fuel (L-gas), but with a significant spread within both ranges; they differ significantly in Wobbe index. These variations are reflected in the reference fuels. 3.1.1. The parent vehicle(s) shall be tested in the test type I on the two extreme reference fuels of Annex IXa. 3.1.1.1. If the transition from one fuel to another is in practice aided through the use of a switch, this switch shall not be used during type approval. In such a case on the manufacturer's request and with the agreement of the technical service the pre-conditioning cycle referred to in point 5.3.1 of Annex III may be extended. 3.1.2. The vehicle(s) is (are) considered to conform if, with both reference fuels, the vehicle complies with the emission limits. 3.1.3. The ratio of emission results "r" should be determined for each pollutant as follows: 01970L0220-20070101_en_img_25 3.2. Exhaust emissions approval of a member of the family:For a member of the family a test of type I shall be performed with one reference fuel. This reference fuel may be either reference fuel. The vehicle is considered to comply if the following requirements are met: 3.2.1. The vehicle complies with the definition of a family member as defined under point 2.2. 3.2.2. The test results for each pollutant will be multiplied with its factor "r" (see point 3.1.3), if r is greater than 1,0. If r is smaller than 1,0, its value will be taken as 1. The results of these multiplications shall be taken as the final emission result. On the manufacturer's request the test type I may be performed on reference fuel 2 or on both reference fuels, so that no correction is needed. 3.2.3. The vehicle shall comply with the emission limits valid for the relevant category for both measured and calculated emissions. 4.GENERAL CONDITIONS 4.1. Tests for conformity of production may be performed with a commercial fuel of which the C3/C4 ratio lies between those of the reference fuels in the case of LPG, or of which the Wobbe index lies between those of the extreme reference fuels in the case of NG. In that case a fuel analysis needs to be present. ANNEX XIII EC TYPE-APPROVAL OF REPLACEMENT CATALYTIC CONVERTER AS SEPARATE TECHNICAL UNIT 1.SCOPE This Annex applies to the EC type-approval, as separate technical units within the meaning of Article 4(1)(d) of Directive 70/156/EEC, of catalytic converters to be fitted on one or more given types of motor vehicles of categories M1 and N1As defined in Annex II Section A to Directive 70/156/EEC. as replacement parts. 2.DEFINITIONS For the purpose of this Annex: 2.1. "original equipment catalytic converter" — see section 2.17 of Annex I; 2.2. "replacement catalytic converter" — see section 2.18 of Annex I; 2.3. "original replacement catalytic converter" — see section 2.19 of Annex I; 2.4. "type of catalytic converter" means catalytic converters which do not differ in such essential aspects as: 2.4.1.number of coated substrates, structure and material; 2.4.2.type of catalytic activity (oxidising, three-way, etc.); 2.4.3.volume, ratio of frontal area and substrate length; 2.4.4.catalyst material content; 2.4.5.catalyst material ratio; 2.4.6.cell density; 2.4.7.dimensions and shape; 2.4.8.thermal protection; 2.5. "vehicle type", see point 2.1 of Annex I; 2.6. "Approval of a replacement catalytic converter" means the approval of a converter intended to be fitted as a replacement part on one or more specific types of vehicles with regard to the limitation of pollutant emissions, noise level and effect on vehicle performance and, where applicable, OBD; 2.7. "deteriorated replacement catalytic converter" is a converter that has been aged or artificially deteriorated to such an extent that it fulfils the requirements laid out in section 1 of Appendix 1 to Annex XI to this DirectiveFor the purpose of the demonstration test of vehicles equipped with positive-ignition engines, when the HC value measured under point 6.2.1 of this Annex is higher than the value measured during type approval of the vehicle, the difference has to be added to the threshold values mentioned in point 3.3.2 of Annex XI, to which the excedence allowed in point 1 of Appendix 1 to Annex XI is applied.. 3.APPLICATION FOR EC TYPE-APPROVAL 3.1. An application for EC type-approval pursuant to Article 3(4) of Directive 70/156/EEC of a type of replacement catalytic converter shall be submitted by the manufacturer. 3.2. A model for the information document is given in Appendix 1 to this Annex. 3.3. In the case of an application for approval of a replacement catalytic converter, the following must be submitted to the technical service responsible for the type-approval test: 3.3.1. Vehicle(s) of a type approved in accordance with Directive 70/220/EEC equipped with a new original equipment catalytic converter. This (these) vehicle(s) shall be selected by the applicant with the agreement of the technical service. It (they) shall comply with the requirements of Section 3 of Annex III to this Directive.The test vehicle(s) shall have no emission control system defects; any excessively worn out or malfunctioning emission-related original part shall be repaired or replaced. The test vehicle(s) shall be tuned properly and set to manufacturer's specification prior to emission testing. 3.3.2. One sample of the type of the replacement catalytic converter. This sample shall be clearly and indelibly marked with the applicant's trade name or mark and its commercial designation. 3.3.3. An additional sample of the type of the replacement catalytic converter, in the case of a replacement catalytic converter intended to be fitted to a vehicle equipped with an OBD system. This sample shall be clearly and indelibly marked with the applicant's trade name or mark and its commercial designation. It must have been deteriorated as defined in point 2.7. 4.GRANTING OF EC TYPE-APPROVAL 4.1.If the relevant requirements are satisfied, EC type-approval pursuant to Article 4(3) of Directive 70/156/EEC shall be granted. 4.2.A model for the EC type-approval certificate is given in Appendix 2 to this Annex. 4.3.An approval number in accordance with Annex VII to Directive 70/156/EEC shall be assigned to each type of replacement catalytic converter approved. The same Member State shall not assign the same number to another replacement catalytic converter type. The same type-approval number may cover the use of that replacement catalytic converter type on a number of different vehicle types. 4.4.If the applicant for type-approval is able to demonstrate to the type-approval authority or technical service that the replacement catalytic converter is of a type indicated in section 1.10 of the Appendix to Annex X to this Directive, the granting of a type-approval certificate shall not be dependent on verification of compliance with the requirements specified in section 6. 5.EC TYPE-APPROVAL MARKING 5.1. Every replacement catalytic converter conforming to the type approved under this Directive as a separate technical unit shall bear an EC type-approval mark. 5.2. This mark shall consist of a rectangle surrounding the letter "e" followed by the distinguishing number or letters of the Member State which has granted the EC type-approval: 1 for Germany 2 for France 3 for Italy 4 for the Netherlands 5 for Sweden 6 for Belgium 7 for Hungary 8 for the Czech Republic 9 for Spain 11 for the United Kingdom 12 for Austria 13 for Luxembourg 17 for Finland 18 for Denmark 19 for Romania 20 for Poland 21 for Portugal 23 for Greece 24 for Ireland 26 for Slovenia 27 for Slovakia 29 for Estonia 32 for Latvia 34 for Bulgaria 36 for Lithuania CY for Cyprus MT for Malta It must also include in the vicinity of the rectangle the "base approval number" contained in point 4 of the type-approval number referred to in Annex VII to Directive 70/156/EEC, preceded by the two figures indicating the sequence number assigned to the most recent major technical amendment to Directive 70/220/EEC on the date EC component type-approval was granted. In this Directive, the sequence number is 01. 5.3. The EC type-approval approval mark referred to in point 5.2 shall be clearly legible and indelible and must, wherever possible, be visible when the replacement catalytic converter is installed on the vehicle. 5.4. Appendix 3 to this Annex gives examples of arrangements of the approval mark and approval data referred to above. 6.REQUIREMENTS 6.1.General requirements 6.1.1.The replacement catalytic converter shall be designed, constructed and capable of being mounted so as to enable the vehicle to comply with the provisions of this Directive, against which it originally complied with, and that the pollutant emissions are effectively limited throughout the normal life of the vehicle under normal conditions of use. 6.1.2.The installation of the replacement catalytic converter shall be at the exact position of the original equipment catalytic converter, and the position on the exhaust line of the oxygen probe(s) and other sensors, if applicable, shall not be modified. 6.1.3.If the original equipment catalytic converter includes thermal protection, the replacement catalytic converter shall include equivalent protection. 6.1.4.The replacement catalytic converter shall be durable, i.e. designed, constructed and capable of being mounted so that reasonable resistance to the corrosion and oxidation phenomena to which it is exposed is obtained, having regard to the conditions of use of the vehicle. 6.2.Requirements regarding emissions The vehicle(s) indicated in point 3.3.1 of this Annex, equipped with a replacement converter of the type for which approval is requested, shall be subjected to a Type I test under the conditions described in the corresponding Annex to this Directive in order to compare its performance with the original equipment catalytic converter according to the procedure described below. 6.2.1.Determination of the basis for comparison The vehicle(s) shall be fitted with a new original equipment catalytic converter (see point 3.3.1) which shall be run in with 12 extra urban cycles (type I test part 2).After this preconditioning, the vehicle(s) shall be kept in a room in which the temperature remains relatively constant between 293 and 303 K (20 °C and 30 °C). This conditioning shall be carried out for at least six hours and continue until the engine oil and coolant temperature are within ± 2 K of the temperature of the room. Subsequently three type I tests shall be made. 6.2.2.Exhaust gas test with replacement catalytic converter The original equipment catalytic converter of the test vehicle(s) shall be replaced by the replacement catalytic converter (see point 3.3.2) which shall be run in with 12 extra urban cycles (type I test part 2).After this preconditioning, the vehicle(s) shall be kept in a room in which the temperature remains relatively constant between 293 and 303 K (20 °C and 30 °C). This conditioning shall be carried out for at least six hours and continue until the engine oil and coolant temperature are within ± 2 K of the temperature of the room. Subsequently three type I tests shall be made. 6.2.3.Evaluation of the emission of pollutants of vehicles equipped with replacement catalytic converters The test vehicle(s) with the original equipment catalytic converter shall comply with the limit values according to the type-approval of the vehicle(s) including, if applicable, the deterioration factors applied during the type-approval of the vehicle(s).The requirements regarding emissions of the vehicle(s) equipped with the replacement catalytic converter shall be deemed to be fulfilled if the results meet, for each regulated pollutant (CO, HC, NOx and particulates) the following conditions:M ≤ 0,85 S + 0,4 GM ≤ Gwhere:M is the mean value of the emissions of one pollutant or the sum of two pollutantsAs appropriate with respect to the limit values defined in point 5.3.1.4 of Annex I to Directive 70/220/EEC in the version against which the vehicle equipped with the original catalytic converter was type-approved. obtained from the three type I tests with the replacement catalytic converter;S is the mean value of the emissions of one pollutant or the sum of two pollutants obtained from the three type I tests with the original catalytic converter;G is the limit value of the emissions of one pollutant or of the sum of two pollutants according to the type-approval of the vehicle(s) divided by, if applicable, the deterioration factors determined in accordance with point 6.4.Where approval is applied for different types of vehicles from the same car manufacturer, and provided that these different types of vehicle are fitted with the same type of original equipment catalytic converter, the type I test may be limited to at least two vehicles selected after agreement with the technical service responsible for approval. 6.3.Requirements regarding noise and exhaust back-pressure The replacement catalytic converter shall satisfy the technical requirements of Annex II to Directive 70/157/EEC. 6.4.Requirements regarding durability The replacement catalytic converter shall comply with the requirements of point 5.3.5 of Annex I to this Directive, i.e. type V test or deterioration factors from the following table for the results of the type I tests.
Table XIII.6.4 Applicable only to vehicles approved to Directive 70/220/EEC, as amended by Directive 98/69/EC or subsequent amending Directives. Applicable only to positive-ignition engined vehicles approved to Directive 70/220/EEC, as amended by Directive 96/69/EC or earlier Directives.
Engine category Deterioration factors
CO HC NOx HC + NOx Particulate
Positive-ignition 1,2 1,2 1,2 1,2
Compression ignition 1,1 1,0 1,0 1,2
6.5.Requirements regarding OBD compatibility (applicable only to replacement catalytic converters intended to be fitted to vehicles equipped with an OBD system) OBD compatibility demonstration is required only when the original catalyst was monitored in the original configuration. 6.5.1.The compatibility of the replacement catalytic converter with the OBD system shall be demonstrated by using the procedures described in Directive 98/69/EC, Annex XI, Appendix 1. 6.5.2.The provisions of Directive 98/69/EC, Annex XI, Appendix 1 applicable to components other than the catalytic converter shall not be applied. 6.5.3.The aftermarket manufacturer may use the same preconditioning and test procedure as used during the original type-approval. In this case, the type-approval authority shall provide, on request and on a non-discriminatory basis, Appendix 2 to the EC type-approval certificate which contains the number and type of preconditioning cycles and the type of test cycle used by the original equipment manufacturer for OBD testing of the catalytic converter. 6.5.4.In order to verify the correct installation and functioning of all other components monitored by the OBD system, the OBD system shall indicate no malfunction and have no stored fault codes prior to the installation of any of the replacement catalytic converters. An evaluation of the status of the OBD system at the end of the tests described in point 6.2.1 of this Annex may be used for this purpose. 6.5.5.The MI (reference section 2.5 of Annex XI to this Directive) must not activate during vehicle operation required by point 6.2.2 of this Annex.
7.DOCUMENTATION 7.1. Each new replacement catalytic converter shall be accompanied by the following information: 7.1.1.the catalyst manufacturer's name or trade mark; 7.1.2.the vehicles (including year of manufacture) for which the replacement catalytic converter is approved, including, where applicable, a marking to identify if the replacement catalytic converter is suitable for fitting to a vehicle that is equipped with an on-board diagnostic (OBD) system; 7.1.3.installation instructions, where necessary. 7.2. This information shall be provided either: as a leaflet accompanying the replacement catalytic converter; or on the packaging in which the replacement catalytic converter is sold; or or by any other applicable means. In any case, the information must be available in the product catalogue distributed to points of sale by the manufacturer of replacement catalytic converters. 8.MODIFICATION OF THE TYPE AND AMENDMENTS TO APPROVALS In the case of modification of the type approved pursuant to this Directive, the provisions of Article 5 of Directive 70/156/EEC shall apply. 9.CONFORMITY OF PRODUCTION Measures to ensure the conformity of production shall be taken in accordance with the provisions laid down in Article 10 of Directive 70/156/EEC. 9.2.Special provisions 9.2.1.The checks referred to in point 2.2 of Annex X to Directive 70/156/EEC shall include compliance with the characteristics as defined under point 2.4 to this Annex. 9.2.2.For the application of point 3.5 of Annex X to Directive 70/156/EEC, the tests described in point 6.2 of this Annex (requirements regarding emissions) may be carried out. In this case, the holder of the approval may ask, as an alternative, to use as a basis for comparison not the original equipment catalytic converter, but the replacement catalytic converter which was used during the type-approval tests (or another sample that has been proven to conform to the approved type). Emissions values measured with the sample under verification shall then on average not exceed by more than 15 % the mean values measured with the sample used for reference.