2016.06.21 - tcmv and taaeg replies...2016/06/21 · no question reply tcmv 1. is there a...
TRANSCRIPT
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Committee of Inquiry into Emission Measurements in the Automotive Sector
EMIS hearing on 21 June 2016
Replies to the Questionnaire to Commission Representatives on TCMV and TAAEG
No Question Reply
TCMV
1. Is there a difference between the RDE-LDV expert group, the RDE-LDV working group and the RDE taskforce? What are these groups exactly, to which organisation do they report, who participated in these groups and what role did they play in the process? Could you please provide us with a detailed composition per grouping, and any of its subgroups (exact number of members with detailed specification per organisation represented)?
The Real Driving Emission-Light Duty Vehicle (RDE-LDV) working group is the main group set up in January 2011 with the objective to support the development, by the Commission, of a complementary test procedure that ensures that the emissions of regulated pollutants are appropriately controlled under normal conditions of vehicle use. Two expert groups were set up as sub-groups of the RDE-LDV WG (the so-called "RDE-LDV expert groups") to discuss and develop specific aspects: (1) the Task Force on Data Evaluation set up in November 2013 with the mandate to assess the potential data evaluation methods and to further fine-tune them; and (2) the PEMS procedure drafting group set up in June 2014 with the mandate to collect expertise on instrumentation and testing and, based on the initial draft prepared by the JRC, to support the development of the structure of the procedure. The role of these groups is to provide specific advice and expertise to the Commission services with regard to the specific tasks allocated to them. The outcome of the two expert groups is discussed in the RDE-LDV working group. The proposals of the later are then discussed at TCMV level.
The group is open for participation to everyone interested in its work and, in fact, experts representing NGOs, academia, equipment manufacturers and automotive industry associations, as well as Member States' authorities and Commission representatives are participating and contributing to its work. The Composition of the participants is balanced and at the same time reflects the specific tasks of the group and the type of expertise required for completing these tasks. All the representatives are participating on equal footing and a no voting system is applied.
A 013320 20.12.2016
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All the drafts prepared by the two sub-groups are submitted and discussed in the RDE-LDV working group and the results are made public via CIRCABC. There is only one section in the group library to which access is restricted, i.e. the one covering the work of the Task Force on Data Evaluation. Due to the sensitivity of some of the data in this section, access is only given by request and has been provided to various stakeholder groups who are contributing to its work. These include industry, Member States, academia and NGOs.
Detailed information on the RDE-LDV working group and its sub-groups is provided in Annex I. All the information concerning the profile of each organisation represented in the RDE-LDV Working Group is publicly available and can be found on the respective organisation's website.
2. At the Commission level the car industry is actively participating in the work of various "expert groups" providing "expertise" and technical advice. While it is clear that the car industry has a lot of useful expertise on the subject, which clearly should be taken advantage of, the influence the industry has on the final version of proposed legislative measures is rather worrying. Do you see any conflict of interest that occurs when those being regulated have vital influence on the regulation itself? Should representatives from the car industry only be consulted at an initial consultative stage of the process and further on any contact should be prohibited?
The Commission acts in the general European interest, not in the interests of any specific group or stakeholder. Stakeholder consultations are integral to well-informed decision-making and serve to improve the quality of EU law making. In this context, it is natural that the Commission closely interacts with a wide range of stakeholders and seeks their views on how to best design the regulatory framework. This has also been the case in the course of preparation of the RDE regulation, where the Commission services regularly consulted industry, Member States, research institutions and NGOs.
However, stakeholders' input only represents a fraction of the information being assessed by the Commission when preparing a legislative proposal, which includes scientific and technical publications, results from EU funded research projects, JRC studies, etc. Hence, consulting stakeholders does not prevent the Commission from taking its decisions independently and autonomously. The Commission therefore does not consider stakeholder consultation as a potential conflict of interest or as a threat to its integrity.
An example of how industry suggestions were treated by the Commission services in the preparation of the RDE is provided in the table attached to Annex I. It shows how the Commission dealt with comments from the European Automobile Manufacturers' Association (ACEA), the main representative of car manufacturers at European level, with regard to key elements of the 2nd Regulation on Real Driving Emissions (RDE), namely the trip definition, boundary conditions and the transfer functions. None of the suggestions to weaken the draft Regulation were taken on board. All the discussions were taking place at
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the RDE-LDV working group and were led by evidence-based arguments.
3. During the work of the TCMV committee, ACEA made
several demands which were aimed at weakening the
more stringent and therefore more-difficult-to-comply-
with testing conditions, which, ACEA claimed had
nothing to do with realistic car use. For instance less
time spent testing in towns or on motorways, narrower
boundary conditions, exclusion of cold start emissions
in the first package, emissions after prolonged stops not
counted, no high-speed tests etc. How does the TCMV
work when faced with such demands? Do you bring
independent experts that can present scientific and
technical facts? Or is the work of the technical
committee more political than technical?
During the deliberations within TCMV, any views, suggestions and recommendations from different
sources (including industry and/or independent experts), can be brought to the attention of the
Committee by any Member State and/or the Commission that are the only members of the TCMV
unlike the industry which is not represented in the Committee. In addition, Member States are free
to request additional technical or scientific expertise from the Commission or any other relevant
external stakeholder, where deemed necessary.
An example of how the Commission dealt with ACEA comments in the broader context of the TCMV's work is provided in the response to Question 2 above.
4. We understand that on 31 January 2011 DG Enterprise
organised the kick-off meeting of the RDE-LDV working
group whose objective was to develop a
complementary test procedure that ensures that the
emissions of regulated pollutants are appropriately
controlled under normal conditions of vehicle use. This
took place four years after the adoption of the 2007
Euro 5/6 Regulation, which mandated the Commission
to keep the test cycle under review.
We understand that between the beginning of 31 January 2011 and the end 2012 four candidate procedures were initially discussed in the RDE-LDV working group:
The Euro 5 requirements apply from September 2009 to new types of vehicles and from January 2011 to all newly produced vehicles. The Euro 6 requirements apply from September 2014 to new types of vehicles and from September 2015 to all newly produced vehicles. The provisions of Article 14 of Regulation (EC) 715/2007 make the emission test procedures conditional to a review of the emissions of Euro 5/6 vehicles. However, an assessment could only be completed once a significant number of Euro 5 vehicles were available on the market. In this regard, the outcome of the first study delivered by the JRC in 2011 was needed to provide the necessary scientific evidence and testing data for the development of real driving emission test procedures.
The RDE-LDV working group looked into four potential approaches to improve the future real driving emission (RDE) test procedures in the context of type-approval (multi-cycle testing like in the US, emissions modelling, random driving cycles and on-road emissions testing with PEMS).
Approach (i) was very much favoured and claimed to be effective by industry. It was
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i. multi-cycle test approach like in the US,
ii. emissions modelling,
iii. random driving cycles,
iv. on-road emissions testing with Portable Emissions Measurement Systems (PEMS).
After that, only the two latter options were taken forward for further consideration. Only in October 2013 the work continued with a dedicated RDE task force focusing on the last option. Why did you need two years, from the beginning of 2011 until the end of 2012, in order to narrow down four options to two options?
considered to assess and test an "honest" (i.e. realistic) environment since it would in principle require the optimisation of emission control over a large area of the engine map. However, it would still leave the possibility for the use of "defeat devices", i.e. cycle sensing and subsequent adaptation of NOx control. This approach was rejected by the Commission and national regulators due to the serious concerns regarding the possible use of defeat devices. An example for this doubt is that it would have been possible for car manufacturers to reduce the level of emission control at temperatures below the lab test temperature or at driving patterns not corresponding to a regulatory cycle.
Approach (ii) was not followed up further because at that time it was not considered as technically feasible.
Approach (iii) would have offered widely randomised cycle conditions and hence it would be more difficult for car manufacturers to identify and predict these cycles. In principle, this would have reduced the risk of defeat devices. Nevertheless, the possibility of cycle sensing could not be totally excluded and hence it was not further pursued.
Approach (iv), i.e. the measurement of emissions on the road, was overall considered as the most robust approach and was hence retained. However, it was necessary to define a complex structure of boundary conditions to ensure unbiased driving (see Annex I). Instead of calculating boundary conditions, the Commission also considered the possibility of supplementing the RDE test procedure with random cycle testing, since this random cycle testing would have been calculated automatically, without any human interventions. However, in light of the identified disadvantages outlined above, this approach was abandoned.
It should be noted that by early 2012, the Commission had narrowed down the four options to two options (on road testing/PEMS + random test cycle), despite heavy criticism of the industry which favoured the US approach (multi-cycle testing). Once this decision was taken, several options of combining these two methods for the different stages of the type approval were discussed (e.g. use random test cycle for the initial type approval test and PEMS testing for the validation testing; or use the random test cycle for PN testing and PEMS for NOx testing) in the course of the year 2012 until early 2013. In the end, for reasons of simplicity and regulatory trust, only the on-road testing with PEMS technology
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was retained.
5. When exactly did the Commission begin to examine
whether the New European Driving Cycle was still
contemporary or needed readjustments?
Regulation (EC) No 715/2007 requires the Commission to keep under review the representativeness of the test cycles and test procedures. The need for a new more realistic test procedure became apparent already from the entry into force of that Regulation and the Commission therefore immediately supported the work that was initiated in 2008 at the United Nations Economic Commission for Europe (UN/ECE) in developing a new more representative laboratory test procedure – the World Harmonised Light Vehicle Test Procedure. The WLTP was agreed at UNECE level in March 2014 and the Commission is now proposing to replace the New European Drive Cycle (NEDC) and introduce the WLTP for the purpose of CO2 and fuel consumption testing from 1 September 2017.
The WLTP is expected to significantly reduce the difference between the CO2 emissions measured in the laboratory and those measured under real driving conditions. It will provide a drive cycle that is more representative of EU driving conditions and a test procedure that is more strictly defined, minimising the use of tolerances and reducing the difference in technology performance between the test and real-world conditions.
The Commission has also commissioned several studies to better understand the gaps between the CO2 emissions measured NEDC and real-world emissions and these results have fed into the development of the WLTP. The results will also be of importance to understand how to ensure that the new procedure continues to reflect real driving conditions over time.
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6. Was the Commission already aware of the temperature-sensing software that reduces the efficiency of emission reduction systems in cars, or the use as defeat devices, as well as other devices with the same function? If they were, since when and what was known? Has the Commission been in contact with the manufacturers regarding this matter? If that is the case, when was this topic first discussed in the working groups with inclusion of the member states?
No. The Commission was not aware of any instances of use of defeat devices.
Please also refer to the written reply to Question 3a of the EMIS Committee questionnaire provided by DG JRC prior to the hearing on 19 April 2016. 1
1 Question 3a: In 2013, two years before the Volkswagen scandal, you had warned EU officials of the dangers of defeat devices. What was the basis for your reference to the
possible use of defeat devices by car manufactures in your 2013 report?
Response: The 2013 report had the objective to assess random cycles and on-road testing with PEMS as two RDE candidate procedures. The assessment was based on
emissions tests conducted at the JRC and expert judgement. The on-road emission measurements reported by JRC did not allow to establish whether the elevated NOx
emissions were due to insufficient emission control, just "negligent" calibration thereof, or an intentional manipulation of vehicles. The JRC did not have any concrete
information that car manufacturers applied illegal defeat strategies at any point in time. Specific search for defeat devices was not in the scope of the JRC work; testing for
the existence of illegal defeat devices according to the legal definition would have required a much deeper and more sophisticated analysis, for which resources (e.g. special
IT knowledge) were not available.
The JRC was aware of the possibility that defeat devices could, in principle, be applied. In 1998, US-EPA accused several US heavy-duty vehicle manufacturers of violating
the Clean Air Act by installing illegal defeat devices. As part of the resulting settlement with the EPA, these manufacturers received heavy fines and were subjected to new
emissions standards which included on-road testing. A subsequent law suit in 2001 was settled in 2003 with a general agreement between heavy-duty vehicle
manufacturers and EPA on provisions of on-road emissions testing with PEMS. In Europe, Regulation 715/2007 explicitly prohibits defeat devices, thus implicitly deducing
that such devices could also be applied in light-duty vehicles, in particular with vehicle control software becoming increasingly sophisticated. Against this background, the
2013 report by the JRC concluded that random cycle testing in the laboratory may be less robust than on-road testing with respect to the application of defeat strategies.
This conclusion, alongside the explanations in Box 2 of the 2013 JRC Report, is derived from Regulation 715/2007, past experiences and a risk assessment based on expert
judgement and deductive reasoning.
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7. According to your knowledge, why were car manufacturers not obliged to disclose if they have used the exemptions for defeat devices provided for in Article 5(2) of Regulation (EC) 715/2007?
Manufacturers have the obligation to respect the law and EU Member States have the standing obligation to enforce it. This also applies to the ban on the use of defeat devices.
In Regulation (EC) 715/2007, there is no explicit requirement for manufacturers to disclose relevant information on whether they make use of the exemptions under Article 5(2). After the VW revelations, the Commission provided in the 2nd RDE Regulation (EU) 646/2016 for the obligation of the car manufacturers to declare their emission reduction strategy.
8. Did the TCMV discuss the public reports regarding the
significant and increasing discrepancies observed in
PEMS tests in real world riving as regards NOx
emissions compared to the legal limits? Did the
Commission or representatives of Member States’
authorities express their intention to pursue with
compliance action, or was there perhaps a coordinated
view not to pursue the evidence of NOx exceedances?
Did the Commission present a legal or other advice on
what type of compliance action should be taken?
The 2011 and 2013 studies of the JRC have been made publicly available and their content was discussed with Member States and stakeholders when developing the RDE test procedure in the RDE-LDV Working Group (2011-2013) and in the TCMV (2014-2015). Neither the Commission services nor the Member States' representatives in the TCMV had, at the time, expressed any specific intention to pursue (or not) compliance actions due to NOx exceedances, since the type-approval framework which both the Commission and the national authorities of the Member States are implementing and ensuring compliance with requires the NOx limits to be met in the laboratory tests set out in Union law. Commission services were of the opinion (as concluded in the 2013 JRC study) that the best way to minimize high real driving emissions was through the development of RDE procedure. High on-road emissions due to potential illegal defeat devices, as described in Union law, therefore remained very much in focus.
In 2012 the Commission sent letters to all Member States stressing the need to enhance market surveillance mechanisms and to ensure that Member States had the necessary structures and resources in place to identify and take corrective actions in relation to vehicles that either did not comply with the relevant EU type-approval requirements, or were representing a serious risk to safety and the environment.
9. So-called on-board-diagnostic-systems (OBD) are
necessary for precise monitoring of in-use emissions.
Does the Commission receive dimensional results from
the OBD-systems? Who else has access to those
results? Do the dimensional results indicate deviations
of the exhaust emissions even when the emissions
OBD provides information and data stored and displayed in individual vehicles. Their main purpose is to alert the driver in case of technical failures and deterioration of components leading to a failure of emission control with respect to the level of a "new" vehicle. These data are not collected systematically or centrally, therefore neither the Commission nor national authorities are in possession of comprehensive OBD data. Manufacturers may of course collect OBD data, e.g. during regular technical maintenance or periodic inspections. Contrary to the US there is no obligation in Europe to communicate such data to authorities
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exceed the set limits? Does the Commission have in-
depth knowledge of the involved software (source
codes) and the measuring parameters?
in a systematic manner (the only exemption being in-use-performance ratios (IUPR), which provide some information about the statistical functioning of OBD in real traffic, but not on actually identified failures).
It should be noted that OBD systems in most cases do not measure emissions directly, they rather measure other parameters (e.g. the pressure loss at a particle filter) allowing conclusions to be drawn on the malfunctioning of these components with respect to their proper state on the basis of modelling. By their very definition, OBD systems are not suitable for monitoring real emissions, their purpose is different. A "new" vehicle with emission control systems installed, as intended by the manufacturer, would never produce OBD alerts, even if the emissions of this vehicle were very high in real driving.
The Commission does not receive sufficient information from manufacturers to acquire in-depth knowledge about OBD software.
10. The ICCT has recently published initial results of the diesel emissions screening campaign conducted by the French, UK and German governments (links below). Can you provide us with more details on the French testing where the results were anonymized? Especially which cars were tested and with which results? Can you elaborate on whether and why the same car models scored differently in each test? http://www.theicct.org/blogs/staff/first-look-results-post-vw-diesel-vehicle-testing-france-uk http://www.theicct.org/blogs/staff/first-look-results-german-transport-ministrys-post-vw-vehicle-testing
The Commission does not have any more information on the French testing than what was made publicly available. While the Commission has repeatedly asked relevant Member States authorities for full access to the results of their investigations, none of them has provided it with technical information beyond that in publicly available reports.
The Commission is currently analysing all reports and data received and we intend to provide a separate report at the end of the investigation period, when all the data from national investigations are available.
11. What exactly happened in the meeting of 28 October 2015 when the conformity factor (i.e. the multiplier used to calculate the allowable emissions during the on-road test with respect to the Euro 6 limit) was raised
In view of the vote on the 2nd RDE Regulation, Commission services prepared an analysis of the future regulatory RDE conformity factors (CF), details of which could be explained in a separate document. The most challenging part of the analysis consisted in taking into account several sources of error, in particular statistical errors of the test procedure2 and of
2 A conformity factor (CF) defines an upper limit for the emissions during a PEMS trip, while the regulatory emission limit roughly corresponds to the average
emissions of all PEMS trips.
http://www.theicct.org/blogs/staff/first-look-results-post-vw-diesel-vehicle-testing-france-ukhttp://www.theicct.org/blogs/staff/first-look-results-post-vw-diesel-vehicle-testing-france-ukhttp://www.theicct.org/blogs/staff/first-look-results-german-transport-ministrys-post-vw-vehicle-testinghttp://www.theicct.org/blogs/staff/first-look-results-german-transport-ministrys-post-vw-vehicle-testing
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from 1.6 to 2.1 for the first stage of application of the regulation, and from 1.2 to 1.5 for the second phase? The original lower CFs proposed by the Commission indicate that it is technically feasible to have lower factors. In fact, already at this early stage in the work of the EMIS committee we had several speakers confirming that the European car manufacturers can deliver clean cars respecting EU legal NOx limits in real world driving without any necessary adjustments (conformity factors) as introduced in the new RDE test. How is the aim of a high level of environmental protection in the Euro 6 regulation now being implemented?
According to the Commission, are the agreed
conformity factors, in the light of technical expertise
presented by several organisations, justifiable? Why the
technical committee's decision concerning RDE does
not reflect scientific facts?
the measurement equipment. It has to be understood that due to these sources of uncertainty one may not assume that the emission limit defined in Regulation (EC) 715/2007 for normal conditions of use of a vehicle would imply a CF equal to 1. On the basis of this technical analysis, possible ranges for the CF were identified.
The initial Commission draft was very ambitious as it was based on CFs identified at the lower end of identified ranges and thus corresponded to the strongest environmental objectives. This draft had to be modified towards higher CFs, within the limits of the identified ranges, in order to obtain a qualified majority in support of the proposal by EU Member States during the TCMV meeting. The agreed CFs remain within the initial ranges identified by the Commission (between 1,6 and 2,2 for the 1st step and a margin between 0,2 and 0,6 for the 2nd step). The Regulation adopted by the Commission was afterwards subjected to the right of scrutiny by the European Parliament and the Council, neither of which opposed to it.
There will be an annual review of the portable measurement technology that will be used for potentially reducing the value of the margin in the definition of the CF. In its statement "Towards comprehensive and efficient emission testing in the EU", the Commission committed to make use of this revision clause to reduce the second conformity factor already in 2017 and on an annual basis. The respective legal obligation for performing this review is explicitly included in the 2nd RDE Regulation.
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No Question Reply
TAAEG
1. What are the differences between national authorities type-approval (e.g. extent to which the testing is done by private companies and whether their links with the automobile industry are somehow monitored; whether it was aware of the use of defeat devices and whether and how they had been justified by auto manufacturers)? Was TAAE aware of that the different practices between national authorities could lead to strategic selection of approval-sites (e.g. How it would account for the fact that the auto industry would not authorize its vehicles where they would be sold or produced, but where lower standards were the norm). Could the TAAE define those practices ("golden cars", defeat devices, testing temperatures etc.) that could most likely be used to deviate testing results from real driving emissions, and to what extent they were used by company/by country?
Technical services are designated by Type-approval authorities (TAA) to carry out tests on their behalf. The national administrative organisation of Member States, as such, has not been discussed in the Type-approval Authorities Expert Group (TAAEG). Its work focuses on technical questions.
TAAEG was set up in 2010 by the Commission in the form of a consultative body composed of representatives of the national type-approval authorities to assist the Commission and Member States in implementing harmonised practices across the internal market. Therefore, TAAEG is aware of possible different interpretations of the law. Questions in TAAEG are raised by the Commission or by Member States, usually after having been discussed in the so-called Type Approval Authorities Meetings "TAAM" where only Member States are present. TAAEG operates in an informal setting and thus cannot take any binding decisions. Its purpose lies not in decision taking at all, but rather in an exchange of information.
The use of "golden cars" has not been discussed in TAAEG. Neither were defeat device and cycle beating before the VW revelations. Differences between laboratory test results and on-road test results have been /are being addressed through the introduction of a more representative test cycle (WLTP) and of a real driving emissions (RDE) testing.
2. Please explain from your point of view why many manufacturers are requesting type-approvals be carried out in Luxembourg or Malta - countries without any car production? What could be the
Information on the number of type-approvals granted by Member States during 2009-2014 can be found in the impact assessment of the recent proposal for a Regulation on type approval of motor vehicles and market surveillance3. During
3 http://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:52016SC0009 Please note, there is a typo on the dates as the reference period covered is 2009-2014 and not 2009-2011 as indicated in the impact assessment.
http://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:52016SC0009
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reasons for that? How many vehicle types have been certified in these countries in the last five years?
this period, 1002 approvals were issued by Luxembourg (2nd biggest figure in the EU after Germany with 1209 approvals granted) and 344 approvals were granted by Malta (6th biggest figure in the EU).
The impact assessment points out that the distribution of the numbers of approvals granted by each Member State "simply indicate that the technical and administrative capacity to carry out verification testing and to issue type-approvals is unevenly distributed in the EU and not always focussed in the main producer countries. However, it could also be related to differences in the stringency that type-approval authorities and their technical services apply, which could induce applicants to selectively apply for type-approval with those approval authorities who are likely to be the most lenient. Therefore, it is important, to ensure that the observed pattern is not the result of unfair competition between national type-approval authorities and their technical services. In order to be able to better verify this in the future, more data from an improved monitoring of these bodies would be highly useful."
3. Which concrete results has the Type-Approval Authorities Expert
Group so far delivered with regard to a more harmonised
interpretation and application of the current rules? When exactly
and in which form has the Commission reminded the Member
States and/or their type-approval authorities of their standing
obligations and recalled the need to establish effective market
surveillance mechanisms at their territories? Please list the
respective results, the Commission's reminders as well as
reactions of the Member States.
The work of TAAEG usually results in a reply to a particular question or highlights the need for the Commission to clarify the legislation via future amendments. Several concrete results can be found in the TAAEG minutes (publicly available) where the Commission reminded Member States of the requirements under the EU legislation, e.g. concerning the harmonized application of Regulation (EC) 661/2009 on vehicle general safety and the implementation of Directive 2006/40/EC (MAC).
4. Which measures have been adopted by the Commission to verify that national authorities granted type approval reflecting real driving conditions? Could you explain the role of the Commission in ensuring that car manufacturers got type approval on vehicles fully reflecting those that will be then placed on the market? According to your knowledge, has the Commission ever checked
The Commission is entrusted with legislative initiative and supervision of the implementation of EU law in the Member States. The existing EU legislation on type approval does not provide a role for the Commission during the actual type approval process. As a consequence, the Commission cannot directly verify that vehicles approved by national authorities and placed on the market comply with their approved type, including as regards their real driving emissions. The
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whether the cars receiving clearance for type approval were exactly the same as the ones placed on the market and driven in real world conditions? Which measures in general were adopted by the Commission to verify the correct implementation of the law with respect to emissions limits?
Commission can only take indirect actions, by launching infringement proceedings against the relevant Member States when it has court proof evidence that they fail to act against non-compliant products. One example of such an (on-going) infringement procedure in the automotive sector concerns the alleged failure of Germany to ensure the effective implementation of the Directive 2006/40/EC on Mobile Air Conditioning (MAC).
The Commission's recent proposal for a Regulation on the type approval of motor vehicles and market surveillance would, if adopted as proposed, significantly change the current situation by entitling the Commission services to carry out checks on vehicles placed on the market and to directly impose penalties in case of non-compliance.
5. What kind of relationship do car manufacturers, type approval
authorities, technical services and laboratories have with each
other? Is there a possible conflict of interests between the car
manufacturers and technical services? If there is, was the
Commission aware of any instances and was this issue ever raised
in the Expert Group? For example, sometimes car companies
operate as technical services. The UK's Vehicle Certification
Agency (VCA) has accredited a facility called JLR Product
Compliance Centre Emission Test Laboratory. This shares its
address with the car manufacturing plant of Jaguar Land Rover
(JLR). Do you know if the JLR test lab also tests Jaguar or Land
Rover cars for type approval? Do you believe this would
constitute a conflict of interest? If a car company also owns and
runs accredited technical services, is this within the current type
approval rules? Will this be allowed under the new rules
proposed by the Commission in their proposal for a new type
approval framework? How will the new proposal ensure there
are no conflicts of interest? Who oversees self-testing by car
The Commission has no concrete indications of a direct conflict of interests or collusion between car manufacturers and technical services. It is common practice in most of the regulated product sectors that the manufacturer pays for the compliance costs for authorising its products for placing on the market. Currently, manufacturers pay a fee directly to the technical services for the type approval testing that these technical services carry out for them. Technical services are dependent on these revenues and compete for this work.
However, given the potential conflict of interest arising from the possible financial links between technical services and manufacturers, and to preserve the independence of testing, the Commission proposed to modify the existing remuneration system in its proposal for a Regulation on the type-approval and market surveillance. The proposal was, inter alia, presented to TAAEG for consultation and comments.
Under the new rules, technical services would no longer receive direct payments from manufacturers but instead all fees would be collected by the Member States. Member States would have to establish a comprehensive national fee structure. This would cover the costs of testing and inspections carried out by the technical services they have designated, as well as to cover the costs of the certification, market surveillance activities and conformity of production review assessments. The proposal also foresees more stringent
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manufacturers? Why wasn't the independence of technical tests
strengthened earlier at a European level?
performance criteria for technical services. They will be regularly and independently audited to obtain and maintain their designation.
The reference to JLR is not accurate. JLR was notified by the UK as a technical service for individual approvals, not for type-approvals. Individual approval is a procedure used to certify a vehicle by a particular person. Self-testing is allowed for a limited number of simple issues (e.g. space for the registration plate) by the current framework as well as by the new text (see list of Annex XV). It does not concern emissions. It is normally not applicable to large volume manufacturers because it is too costly and lengthy in time. So it is not about self-testing but to provide testing facilities close to home for citizens.
Testing on the premises of the manufacturer for practical reasons (lack of test houses), is also allowed by both the current and the proposed framework; however, these tests are performed or supervised by a 'real technical service'.
6. It has been a common knowledge that car industry uses practices
that, whilst not against the law, are certainly not in the spirit of
the law (for instance preparing 'golden cars' for tests or use of
defeat devices).The new Regulation on type-approval does not
clarify the issue of defeat devices, which are being widely
misused by manufacturers due to a lack of clarity over how a
defeat device is defined. Could you please explain why the final
text does not include a concrete definition of what constitutes a
defeat device including obligations for car manufacturers to
disclose and justify the installation of any auxiliary devices, which
change the normal functioning of a vehicle? Could you please
explain why the final text does not include any provisions
prohibiting too flexible interpretation of the Regulation by the
manufacturers and thus making the use of 'golden cars' illegal?
Since Regulation (EU) 715/2007 entered into force, the Commission has not
received a single request from Member States' authorities or industry
representatives pointing to the need to clarify its provisions. The Regulation
already contains a definition and rules for defeat devices that provide sufficient
legal clarity, even if the implementation faces certain factual/technical
challenges. In order to ensure a coherent/ uniformly effective implementation
of this ban of defeat devices across all Member States, the Commission has
provided for an obligation for car manufacturers to disclose and justify the
installation of devices under Article 5(2) in the 2nd RDE Regulation (EU)
646/2016.
The issue of "golden cars" is different from the use of defeat devices. The
practice of using "golden cars" for type approval is addressed through the
introduction of RDE and WLTP.
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7. Which type-approval authorities of the Member States are
already now executing regular ex post checks of cars in
circulation? Which are the Member States with effective and
sufficient market surveillance to control the conformity of cars
already in use?
Checks on cars already in circulation are carried out in accordance with Directive 2009/40/EC4, repealed by Directive 2014/45/EU5 from 20 May 2018, which requires each Member State to ensure that vehicles registered in its territory are periodically tested by testing centres authorised by the Member State in which those vehicles are registered. Roadworthiness tests may be carried out by a public body entrusted with the task by the Member State or by bodies or establishments designated and supervised by that Member State, including authorised private bodies. Testing of exhaust emissions is included in the list of minimum requirements to be checked within the roadworthiness tests.
As regards vehicles placed on the market, the market surveillance authorities of the Member States are responsible for ensuring that those vehicles are in conformity with their approved type. Market surveillance is organised at national level and Member States are required to ensure an appropriate set of infrastructures for that purpose and to prepare national market surveillance programmes. The responsibilities of the national market surveillance authorities include the tasks of keeping citizens informed about potential risks and ensuring that corrective measures (including bans, withdrawals, recalls or any other measures that ensure that conformity is re-established) are taken against non-compliant products. The level of the sanctions is also determined at national level.
In 2012, the Commission reminded the Member States of their obligation to establish on their territories effective market surveillance systems and to ensure that the necessary structures and resources are put in place to identify and take corrective actions in relation to vehicles that either do not comply with the relevant EU type-approval requirements, or represent a serious risk to safety and the environment.
4 OJ L 141, 6.6.2009, p. 12.
5 OJ L127, 29/4.2014, p. 51.
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8. The Commission describes the task of your expert group on its website as to "monitor the development of national policies and the enforcement of EU legislation by national authorities". Did you monitor the enforcement of the Commission's regulation from the year 2007 prohibiting defeat devices after your in-house colleagues from the Joint Research Centre pointed out in 2011 and 2013 that such devices were being used?
The Commission was not aware of any instances of use of defeat devices before the outbreak of the VW scandal. The statement that the JRC reports from 2011 and 2013 indicated that such devices were being used is factually wrong. In fact, the 2011 report only concludes that "the results indicate that NOX emissions of light-duty diesel vehicles substantially exceed the Euro 3-5 emission limits: by a factor of 4-7 as averages over entire test routes and up to a factor of 14 for individual averaging windows. The increasing stringency of European emission limits has, thus, not resulted in an equivalent reduction of on-road NOX emissions of light-duty diesel vehicles." Further on, the 2013 Report points out that "PEMS appears to be more effective in preventing the detection of emissions tests by vehicles and thus the use of defeat strategies under normal conditions of vehicle use", however, it does not suggest or provide any evidence that defeat devices might have been used on the tested vehicles.
9. Could you please provide an overview for the 15 most sold diesel models in the European Union in 2011, 2012, 2013, 2014 and 2015 providing information on where and by which organisation the emissions, emissions-related technologies and the engines of the models were tested (the relevant test organisations) and type approved (the relevant type approval authorities for pre-production type approval)?
The Commission does not have the information requested by the European Parliament. Member States are not obliged to provide such information under the current legislation. In the new Regulation for type-approval of motor vehicles and market surveillance it is proposed that Member States make available to the Commission all data related to the type-approval by establishing a database.
General information on the most sold models of vehicles in Europe is however available on the Internet.
10. Could you also indicate which Conformity of Production (CoP)
checks and In-service conformity (ISC) checks were carried out for
these models, and by which organisation? Were for these models
supplementary checks carried out by the national authorities
(independent from the check by car manufacturers)? If yes,
which national authority and when?
These questions need to be addressed to the respective TAA who approved the
vehicles concerned. The Commission is not in the position to provide this
information.
11. Did the TAA Expert group discuss the public reports regarding the
significant and increasing discrepancies observed in PEMS tests in
No, these issues were not discussed in the TAAEG meetings before the
outbreak of the VW scandal, as they were discussed with Member States in the
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real world driving as regards NOx emissions compared to the
legal limits? Did the Commission or representatives of Member
States’ authorities express their intention to pursue with
compliance action, or was there perhaps a coordinated view not
to pursue the evidence of NOx exceedances? Did the Commission
present legal or other advice on what type of compliance action
should be taken?
context of other platforms (for example the TCMV).
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Annex I Explanatory note on RDE-LDV Working Group and its expert sub-groups
The European Commission has the standing obligation to carry out broad consultations with
interested parties in order to ensure that the Union's actions are coherent and transparent (Article
11(3) of TFEU). Moreover, the consultation mechanisms form part of its activities throughout the
whole legislative process, from policy-shaping prior to a Commission proposal to final adoption
of a measure by legislators and implementation. Depending on the issues at stake, consultation is
intended to provide opportunities for input from representatives of undertakings and associations
of undertakings, NGOs, academics, national authorities, technical experts and other interested
parties.
In this context, the RDE-LDV Working Group and its sub-groups were established to support the
development process of a procedure specifically assessing the real driving emissions of light duty
vehicles in a robust manner with a view to its regulatory implementation. In particular, the RDE-
LDV WG was set up with the aim to provide technical advice and a platform for exchange of
information and contributions of stakeholders to accompany and support the process of
development of the RDE test procedure by the JRC. Therefore, the work of the Group is focussed
on technical issues only, while all policy and legal elements remain outside the scope of its
activities (they are handled by the Commission within its internal procedures).
In the RDE case, the need to collaborate and consult with stakeholders prior to (or in parallel
with) the preparation of the draft legal act stems from the very technical and pioneering nature of
the issues at stake which requires access to important inside expertise, knowledge and data
available to those stakeholders. Such an approach is fully in line with the principles of Better
Regulation. Evidence-based legislation can only be achieved in discussions with those who have
the practical expertise. In addition, the role of the Group to provide specific advice and expertise
to Commission services on a given subject and in light of a specific mandate fully corresponds to
the key principles for the creation and functioning of Commission expert groups (as indicated in
the Commission Decision establishing horizontal rules on the creation and operation of
Commission expert groups (COM(2016)3301)).
From an organisational point of view, DG ENTR/GROW is supervising the activities of the
Group and drafted its Terms of Reference (the final ToRs are provided separately). The Group
started its work at the beginning of 2011.
The Group is open for participation to everyone interested in its work. A wide spectrum of
experts representing NGOs, academia, equipment manufacturers and automotive industry
associations, as well as Member States' authorities and Commission representatives, have been
participating and contributing to its work (the list of the participants is provided separately). The
composition of the participants is balanced, yet reflects the specific tasks of the Group and the
type of expertise required for completing these tasks. All the representatives are participating on
equal footing and a no voting system applies.
Meetings of the Group aim at consulting the representatives based on the specific expertise and
information they have and at gathering their views on the work-in-progress. However, this does
not commit the Commission to reflect these views in the final draft of the legal acts. All the
technical considerations which resulted from the work of the RDE-LDV WG were carefully
assessed by the Commission in the process of drafting the RDE package and in the following
inter-service consultations. In addition, the consultations of stakeholders need to be distinguished
from the process in the Technical Committee – Motor Vehicles (TCMV), where Member State
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2
representatives are consulted on the draft of the legal act. The Commission may only take the
decision of adopting the final legal act following a positive opinion of the Committee (Article 5
of Decision 1999/468 as amended by Decision 2006/512 and recital (21) to Regulation
182/2011).
In order to further support the RDE-LDV WG, two expert groups were set up as sub-groups to
discuss and develop specific aspects:
The “Task Force on Data Evaluation" has been mandated to assess candidate data
evaluation methods and to further develop/fine-tune them. The data evaluation methods
discussed in the "task force" can be found in Appendices 5 and 6 of the Regulation.
The “PEMS1 procedure drafting group”, whose mandate has been to collect expertise on
instrumentation and testing and, based on the initial proposal made by JRC, to support
the development of the structure of the procedures that can be found in Appendices 1 to 4
of the Regulation.
All the proposals made by the two sub-groups were submitted and discussed in the RDE-LDV
WG and the results were made public via the CIRCABC group "New light duty test procedures:
WLTP, MAC, ...". Access to the group is open to all and does not require any membership or
registration with the CIRCABC system. There is only one section in the CIRCA group Library to
which access is restricted, i.e. the one covering the work of the Task Force on Data Evaluation.
Due to the sensitivity of some of the data in this section, access is only given on request. Access
to the section has been provided to various stakeholder groups who are contributing to the work
of the Task Force. These include industry, Member States, academia and NGOs.
Meetings of the RDE-LDV WG are convened on a regular basis taking into account the
Commission's need for expertise. Usually, they take place in the Commission's premises, but also
frequently via audio/web or video conferences. DG ENTR/GROW managed the organization
(uploading invitations and documents in CIRCABC) and chaired the meetings.
Though some minutes of the meetings are available, they were not drafted systematically for each
and every meeting of the Group due to the following reasons:
a substantial part of the documents were in the form of presentations that are self-
explanatory and were as such made available in CIRCABC;
confidential arrangements, for instance, the Task Force on Data Evaluation that was set
up under the rules of confidentiality because of the sensitivity of the data;
in-case executive summaries (the discussions' quintessence) were prepared.
Examples:
In order to demonstrate how the above process materialises in practice, some examples
concerning three key elements of the RDE package, namely the trip definition, boundary
conditions and the transfer functions, are given below. The examples focus on comments from
the European Automobile Manufacturers' Association (ACEA), which is the main representative
of car manufacturers at European level.
Trip definitions
1 Portable Emission Measurement System (PEMS)
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3
When the conditions of a PEMS trip are defined, a number of parameters must be specified (e.g.
maximum speed, ambient temperatures, altitudes etc.). The table in the Annex explains how the
Commission handled ACEA's comments.
Boundary conditions (provided for in the 2nd
regulatory RDE act)
Due to their very nature, the driving conditions of PEMS trips show a certain variation (this is
actually the main feature rendering the conditions of a PEMS test non-predictable, which is also
the main feature for beating defeat devices). As a consequence, without any further requirements,
in a regulatory environment, PEMS trips risk to be driven in a biased manner, too aggressive or
too soft.
Therefore complementary boundary conditions relating to the dynamics of PEMS trips had to be
included to prevent such biased driving. These boundary conditions had to be chosen is such a
manner that they include a wide range of driving conditions (i.e. it was agreed to cover at least
95% of all PEMS trips, which can be constructed from statistical real driving data). For timing
reasons this development was not finalised for the 1st regulatory RDE act (not a problem since
complementary boundary conditions are not of particular importance if PEMS testing is done
without binding limits - monitoring phase).
For the 2nd
regulatory RDE act boundary conditions were developed in the RDE-LDV (sub-group
data evaluation task force), ensuring on the one hand that PEMS trips are driven with sufficiently
high dynamics (addressing so-to-say the "regulator's risk", e.g. preventing driving with constant
speeds only) and on the other hand not with unnaturally high dynamics (addressing the
"manufacturer's risk" that a vehicle is challenged by a third party not because of its bad emission
performance but because of a biased execution of the test).
There was a wide consensus among experts present at RDE LDV WG meetings about the
way/method of defining complementary boundary conditions, i.e. using upper limits for the 95%-
tile of the second-by-second values of the value (velocity x acceleration) and minimum values for
the RPA. During the discussions on numerical values of these upper limits, ACEA strongly
encouraged the choice of lower values leading to more lenient test conditions. The Commission
services nonetheless decided to use the WLTP2 driving database for deriving values with
sufficient statistical evidence, even increasing them further.
Following the opinion of the TCMV on the 2nd
regulatory RDE act delivered on 28 October 2015,
ACEA suggested further additions to the complementary boundary conditions for light
commercial vehicles (category N1). They claimed that due to their relatively low power/mass
ratio the dynamics of these vehicles at a regulatory PEMS trip should be further constrained. In
February 2016, ACEA was informed in bilateral discussions with Commission services that:
The matter is complex and will only be considered (if at all) at the 4th regulatory RDE
act, since it is only relevant for independent testing by 3rd
parties:
Clear statistical evidence from real driving data has to be provided in order to justify a
special treatment of vehicles with a low power/mass ratio;
The criterion for any special treatment must be an objective technical one, e.g. the
power/mass ratio, rather than a formal one (belonging to a specific vehicles' category).
2 World-wide Harmonised Light-Duty Test Procedure (WLTP)
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4
Transfer functions
Transfer functions are a concept, by which different conformity factors are attributed to PEMS
trips, depending on the severity of the trip. ACEA suggested introducing transfer functions for
the 2nd
regulatory RDE act for the first time in July 2015 (after TCMV delivered its opinion on
the 1st regulatory RDE act). ACEA's initial suggestion was that transfer functions would only
attribute higher conformity factors than the ones published in the legislation if a trip is considered
severe, arguing that such approach would allow a positive public perception of the legislation
while limiting the burden to industry.
It has to be understood that the concept of transfer functions, if applied correctly, offers in
principle the possibility of achieving the same overall emission level at lower costs or a more
demanding emission level for the same costs. So transfer functions are in principle a valid
concept, and this explains why ACEA wanted to draw the Commission’s attention to them.
However, for the Commission it was also clear that transfer functions could only be applied in an
environmentally balanced manner. This means that for some "easy" PEMS trips the regulatory
conformity factor would have to be lower than a "central" value agreed in the legislation, if for
"severe" trips a higher conformity factor should be allowed. The global effect of the transfer
functions on the emissions would at least have to be neutral, to be demonstrated by empirical
statistical driving data.
However, an environmental assessment being very complex, transfer functions were not
considered a mature concept for the 2nd
regulatory RDE act, though it was eventually agreed by
Member States at the TCMV to include a placeholder for possible future inclusion, subject to
strict conditions. The concept of transfer functions may be investigated at the 4th regulatory RDE
act under the condition of an environmentally neutral implementation.
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5
Trip definitions (different positions of ACEA and the Commission services of November 2014)
Reference Current proposal ACEA position Remark
Annex IIIA, 5.1;
vehicle payload
Vehicle may be PEMS
test with up to 90%
of the maximum load
5.1.3 Moderate
vehicle test mass
conditions: The
vehicle test mass shall
not exceed the lowest
of: a) vehicle unladen
mass excluding driver
+200Kg b) 90 % of
GVW or c) 2840Kg
5.1.4 Extended
vehicle test mass
conditions: The
vehicle test mass shall
not exceed the lower
of: a) 90% of GVW or
b) 2840Kg
Current proposal reflects
well the requirement of
compliance with regulatory
emission limits under all
normal conditions of use
and is well supported by
most Member State experts
in the RDE-LDV group.
The ACEA position would be
very complicated to
implement. In addition it
would make PEMS testing
at type approval for
moderate conditions quite
difficult (i.e. driver + witness
+ PEMS equipment < 200
kg)
Annex IIIA,
5.2.4 and 5.2.5,
PEMS ambient
test
temperature
5.2.4. Moderate
temperature
conditions: greater
than or equal to 273K
(0°C) and lower than
or equal to 303K
(30°C)
5.2.5. Extended
temperature
conditions: greater
than or equal to 266
K (-7°C) and lower
than 273 K (0°C) or
greater than 303 K
(30°C) and lower
than or equal to 308
K (35°C)
5.2.4. Moderate
temperature
conditions: greater
than or equal to 282K
(9ºC) and lower than
or equal to 303K
(30°C). (Note: 3 ºC to
be introduced in a
second phase 5 years
after RDE-Regulation
was published within
OJ)
5.2.5. Extended
temperature
conditions: greater
than or equal to 276 K
(3ºC) and lower than
282 K (9°C) and lower
than or equal to 303K
(30°C). (Note: -7ºC
Current proposal
constitutes already a
compromise with respect to
the requirement of
compliance with regulatory
emission limits under all
normal conditions of use
(i.e. basically the
temperature range should
be wider). It is based on the
analysis of metrological
data and well supported by
most Member State experts
in the RDE-LDV group.
The ACEA proposal would
leave a large area of real
driving conditions in the
autumn/winter and in
middle and northern Europe
uncontrolled.
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6
may be introduced
after a cost-
effectiveness analysis
considering a low
temperature CF in a
second phase 5 years
after RDE-Regulation
was published within
OJ)
It should also be noted that
PEMS currently only relates
to driving conditions with a
warm engine since the cold
start is excluded. There is
no technical reason why the
emission performance of
vehicles with a warm engine
should be worse when the
ambient temperature is
lower. If ACEA is concerned
about the handling of the
cold start at lower ambient
temperatures (the cold start
should be included into the
PEMS procedure at some
point), these concerns could
be addressed by a recital.
Annex IIIA, 6.7,
maximum
vehicle velocity
The vehicle shall
normally not exceed
a velocity of 145
km/h. However, for
practical reasons this
velocity may be
exceeded by a
tolerance of 15 km/h
for not more than 3%
of the driven
distance during
motorway driving.
The vehicle shall never
exceed 145 km/h on
open public roads.
The speed range of
the motorway driving
shall properly cover a
range between 90 and
at least 110 km/h. The
vehicle's velocity
should be above 100
km/h for at least 5
minutes.
The vehicle's velocity
above 130 km/h may
be driven for a
maximum of 5 % of
the distance driven on
the motorway if the
legal situations allows
it.
The Commission services
are of the opinion that a
particular limit for the
maximum velocity for PEMS
testing is not necessary, due
to the application of a
normalisation process at
the data evaluation. After
discussions at the RDE-LDV
the Commission services
have nonetheless agreed to
a maximum velocity for
PEMS testing of 160 km/h.
After further comments
from various Member
States at the last TCMV the
Commission services have
lowered this value to 145
km/h.
The suggested marginal
exceedance of this value is
necessary to allow for PEMS
testing "very close" to 145
km/h under practical
conditions (otherwise a very
short, marginal exceedance
of this maximum velocity
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7
would invalidate the entire
PEMS test). In addition, with
respect to the previous
proposal, the high speed
test for "fast" vehicles has
been removed on request
of ACEA.
It should be noted that the
current Commission service
and ACEA proposals are
very close.
Annex IIIA, 6.8,
average urban
driving velocity
at PEMS test
6.8. The average
speed (including
stops) of the urban
driving part of the
trip should be
between 15 and 30
km/h. The vehicle's
speed should be less
than 1 km/h for at
least 10 % of the
time.
6.8. The average
speed (including
stopsidling) of the
urban driving part of
the trip should be
between 25 and 45
km/h. The vehicle's
speed should be less
than 1 km/h for at
least 10 % of the time.
- For practical reasons
with experience from
more than 100 of
PEMS-Trips the
minimum average
speed should not be
lower than 25 km/h.
In addition to that, 80
% of distance
weighted in urban EU-
WLTP is larger than 25
km/h speed.
If the Commission
wants to avoid
constant driving a
separate paragraph
could make this
possible.
The Commission service
proposal is supported by
urban driving data. The
upper limit for the average
velocity of urban driving of
45 km/h (including stops)
suggested by ACEA does not
seem to be appropriate,
given that there is a urban
speed limit of 50 km/h in
most Member States.
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Commission européenne, B-1049 Bruxelles / Europese Commissie, B-1049 Brussel - Belgium. Telephone: (32-2) 299 11 11. Office: BREY 10/000. Telephone: direct line (32-2) 29xxxxx. Fax: (32-2) 29xxxxx. E-mail: @ec.europa.eu
EUROPEAN COMMISSION ENTERPRISE AND INDUSTRY DIRECTORATE-GENERAL Industrial Innovation and Mobility Industries
Automotive industry
Brussels, 26 January 2011 ENTR.F1/xx D(2011)
Working group for the development of a real driving emissions test procedure for
light-duty vehicles (RDE-LDV): scope mandate
(DRAFT !)
1. BACKGROUND
At the workshop on the "future approach to automotive emissions" of 23 November
2010 the Commission (JRC) and some Member States have presented data demon-
strating that Euro 5 vehicles currently being on the market do not comply with regu-
latory emissions limits under real driving conditions. These Euro 5 data confirm
similar data collected previously on Euro 3 and Euro 4 vehicles, which show that
e.g. real driving NOx emissions of light duty diesel vehicles did not change much, if
at all, over the last decade, despite ever more stringent regulatory limit values.
As a consequence Article 14(3) of the Euro 5/6 Regulation 715/2007/EC requires
the Commission to adapt type approval procedures such that they reflect real driving
emissions of regulated pollutants (currently CO, HC, NOx, PM/PN). In this context
Recital (15) makes explicit reference to the use of "portable emission measurement
systems" (PEMS) and "not-to-exceed" regulatory concepts.
The development of procedures specifically assessing the real driving emissions of
regulated pollutants has been excluded from phase 1 of the World Light duty Test
Procedure (WLTP) at UNECE in June 2009. Basically real driving emissions could
be addressed in phase 2 of this process, which runs from 2014 – 2022 (still to be
confirmed by contracting parties). Given the massive air quality problems in the Eu-
ropean Union and the regulatory provisions of Euro 5/6 Regulation 715/207/EC,
supported by the Communication on the application and future development of
Community legislation concerning vehicle emissions from light-duty vehicles (…)
(2008/C 182/08) of 19 July 2008, it is obvious that such a time frame is not accepta-
ble from a European perspective.
Therefore the development of a "RDE-LDV" procedure, which should assess real
driving emissions of light duty vehicles in a robust manner with a view to its regula-
tory implementation at the mandatory Euro 6 dates, is launched at a European level.
It should be emphasised that at the current stage no final decision about the method-
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2
ology of his procedure has been taken, e.g. whether a “PEMS-like” test or other tests
should be used.
The Commission will of course support the consideration of the developed Europe-
an RDE-LDV for a respective globally harmonised procedure in phase 2 of the
WLTP process.
2. MANDATE OF THE RDE-LDV GROUP
The RDE-LDV working group is open to stakeholder experts and should accompany
the development of a RDE-LDV test procedure by the JRC. In particular, the group
should provide technical advice and a platform for the exchange of information and
contributions of stakeholders that will be discussed and agreed during the process.
The group should focus on technical issues of the RDE-LDV test procedure. Politi-
cal elements, e.g. the question of legal implementation for Euro 6 vehicles, will have
to be decided elsewhere.
3. ORGANISATIONAL MATTERS
RDE-LDV working group will meet regularly, according to demand, either face-to-
face or via audio/web or video conferences. A web-based extranet (Circa) will be es-
tablished for the exchange of documents.
Stakeholders will have to provide their own travel costs if they do not receive an ex-
plicit promise of the Commission for coverage of these costs in exceptional cases.
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http://ec.europa.eu/transparency/regexpert/index.cfm?do=groupDetail.groupDetail&groupID=1295
Working Group on Motor Vehicles (E01295)
Subgroup: Real Driving Emissions - Light Duty Vehicles
Organisation
Organisation Name Organisation Type Countries/Areas
represented Membership Status
ACEA - European Automobile Manufacturers'
Association Association European Member
AECC - Association for Emissions Control by
Catalyst Association European Member
AEGPL - European LPG Association
Association European Member
ANEC - European Consumer Voice in
Standardisation NGO European Member
BEE - European Environmental Bureau
NGO European Member
BEUC - European Consumers Organisation
NGO European Member
CEC - European Fuels and Lubricants Performance
Test Development Organistion
Association European Member
CENCENELEC Association European Member
CLEPA - European Association of Automotive
Suppliers Association European Member
DOW Automotive Systems Association International Member
FIA - Fédération Internationale de
l'Automobile NGO European Member
INTA - Instituto Nacional de Técnica Aeroespacial
Research Institute European Member
JAMA - Japan Automobile Manufacturers Association
Association Japan Member
NGVA Europe Association European Member
T & E - Transport & Environment
NGO European Member
TNO - Nederlandse Organisatie voor
Toegepast Natuurwetenschappelijk
Onderzoek
Research Institute European Member
TRL - Technical Research Laboratory
Corporate United Kingdom Member
TüV Nord (Technischer Überwachungsverein - Technical Inspection
Association)
Association European Member
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National administrations
Country Public Authority Membership Status
United Kingdom Department of Transport,Permanent
Representation UK Member
Sweden Permanent Representation SV,Vägverket Member
Netherlands Ministerie van VROM,Permanent
Representation NL,Rijksdienst voor het Wegverkeer
Member
Germany Bundesumweltministerium,Permanent
Representation DE,Verkehrsministerium Member
http://ec.europa.eu/transparency/regexpert/index.cfm?do=groupDetail.groupDetail&groupID=1295http://ec.europa.eu/transparency/regexpert/index.cfm?do=groupDetail.groupDetail&groupID=1295http://ec.europa.eu/transparency/regexpert/index.cfm?do=groupDetail.groupDetail&groupID=1295http://ec.europa.eu/transparency/regexpert/index.cfm?do=groupDetail.groupDetail&groupID=1295
20160621-Commission_TCMV_TAAEG_replies + Annexes.pdf (p.1-16)Annex 1 - Explanatory note on RDE-LDV WG and its expert sub-groups.pdf (p.17-23)Annex - Working Group RDE-LDV Scope Mandate.pdf (p.24-25)Annex - Working Group RDE-LDV - Organisations.pdf (p.26-27)