1

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

2

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

3

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

4

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

5

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.

6

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.

7

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

8

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

9

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.

10

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

11

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

12

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

13

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.

14

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.

15

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

16

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).

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

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)

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)

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.

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.

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

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.

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-

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.

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

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=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=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=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=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=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=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=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=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=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=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=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=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=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=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

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)