Guide to the Approximation of European Union
Environmental Legislation
Air Quality
Air pollutants come from a wide variety of sources, both mobile and
stationary. This Section deals the legislation concerning general air
quality assessment and management and the legislation on controls of emissions
from mobile sources, i.e. transport related emissions from motor vehicles
and fuels.
Legislation on controls of emissions from stationary sources are
dealt with in Section F, , concerning emissions from industrial
installations and power generation, and in Section C, concerning
emissions from waste incinerators.
The new Air Quality Framework Directive is designed to provide a
comprehensive strategy for the management of air quality in Member States
linking controls on emissions with the attainment of air quality objectives.
This Directive will progressively take effects when its forthcoming daughter
directives are adopted and enter into force. These forthcoming
daughter-directives will replace three existing directives which establish
quality standards for sulphur dioxide and particulates, lead, and nitrogen
oxide. Under the Tropospheric Ozone Pollution Directive Member States
also have to set up ozone monitoring networks.
A series of directives control emissions from motor vehicles and fuels
through technical requirements on the vehicles and through limits on the
presence of substances such as lead and sulphur in fuels. Additionally a
Directive on emissions from engines to be installed in mobile machinery is due
to be adopted soon.

B.1 Air Quality Framework Directive
Directive 96/62/EC on ambient air quality assessment and management, known
as the Air Quality Framework Directive, aims to set the basic principles of a
common strategy which:
- Defines and establishes objectives for ambient air quality in the Union in
order to avoid, prevent or reduce harmful effects on human health and the
environment as a whole
- Assesses the ambient air quality in Member States on the basis of common
methods and criteria
- Produces adequate publicly available information about ambient air quality
and ensures that it is available to the public by means of alert thresholds,
etc.
- Maintains ambient air quality where it is good and improves it in other
cases.
Member States are responsible for:
- Implementing the directive
- Assessing ambient air quality
- Ensuring the accuracy of measurement
- Approving measuring devices
- Analysing assessment methods
- Co-ordinating on their territory the Unionwide quality assurance
programmes organised by the Commission.
The framework directive will set key pollution management parameters for the
private sector. New standards will be adopted under the directive which will
replace earlier directives concerning sulphur dioxide and particulates, lead and
nitrogen oxide, described below.
Over a period of ten to fifteen years, optimal ambient air quality limit
values, margins of tolerance, assessment procedures and reporting requirements
will be established for individual pollutants through a series of daughter
directives. The first of these forthcoming daughter directives concerning NO2,
SO2/particulates and lead is foreseen to be adopted by the Commission in
Autumn 1997.
Once limit values and alert thresholds have been determined, ambient air
quality will have to be assessed. Action plans must be drawn up for zones which
do not meet the limit values. Measures must integrate the protection of air,
water and soil and be aimed at meeting deadlines. The public must be informed
when alert thresholds are exceeded.
Implementation considerations
- The directive's requirements presuppose adequate administrative systems,
scientific know how and standards-based regimes for the management of ambient
air quality.
- Countries should compare the framework directive's requirements with
existing national laws and operational systems, existing approaches for
achieving ambient air quality objectives, methodologies for air quality
assessment, the availability of information listed in Annex IV and the means of
improving air quality in order to determine what changes are necessary.
- Often new procedures of consultation between authorities, alignment of
monitoring and measuring methodologies, reporting and assessment will be needed.
- Laboratories must be accredited in a manner consistent with European
standards for quality assurance. Both laboratories and measuring sites must have
organised systematic internal quality controls.
- Air quality improvement plans must be developed for areas of poor air
quality with specific improvement deadlines. The plans may provide for measures
to control or suspend activities such as motor vehicle traffic which contribute
to the limit values being exceeded.
- Representatives from air polluting industries as well as other interested
parties should be consulted on implementation requirements, especially on the
drawing up of the improvement plans so as to smooth the way to compliance with
air quality standards.
B.2 Existing Air Quality Standards which will progressively be replaced by
Daughter Directives under the Framework Directive.
Sulphur Dioxide and Suspended Particulates
Directive 80/779/EEC on air quality limit values and guide values for
sulphur dioxide and suspended particulates established binding annual and winter
limit values and non-binding guide values for sulphur dioxide and suspended
particulates in the atmosphere. Its main purpose was to protect human health and
limit values were based on findings of the World Health Organisation.
Implementation considerations
- Countries need to assess whether there are operational measuring stations
at sites where pollution is expected to be the greatest. Those measuring
stations need to use reference methods for sampling and analysis of sulphur
dioxide and suspended particulates. Additional measuring stations may be
required.
- Procedures need to be put in place to allow data compilation and analysis
at national level and reporting to the Commission.
- Procedures need to be put in place to ensure that in case the
concentrations exceed the limit values in Annex I, the Commission is informed
and plans are developed for the progressive improvement of the quality of air in
those zones. This requires identification of the main sources of pollution and
an assessment of emission reduction possibilities.
Lead
Council Directive 82/884/EEC prescribed a maximum limit value for lead
concentrations in air to protect human health, but insufficient technical and
scientific information was available at the time to set limit values for
environmental protection.
Implementation considerations
- Countries need to assess whether there are operational measuring stations
at sites where individuals may be exposed continually for a long period and
where there is a likelihood that the threshold limit value for lead is exceeded.
Those measuring stations need to use a conforming methods for sampling and
analysis.
- Procedures need to be put in place to allow data compilation and analysis
at national level and annual reporting to the Commission.
- Procedures need to be put in place to ensure that in case the
concentrations exceed the limit values, the Commission is informed and plans are
developed for the progressive improvement of the quality of air in those zones.
This requires identification of the main sources of pollution and an assessment
of emission reduction possibilities.
Nitrogen Oxide
Directive 85/203/EEC laid down binding limit values designed to protect
human health and non-binding guide values to improve the protection of human
health and contribute to the long-term protection of the environment. The guide
values are intended to serve as reference points for the establishment of
specific schemes in zones determined by the Member States.
Implementation considerations
- Countries need to assess whether there are operational measuring stations
at sites where the limit value is likely to be exceeded. Additional measuring
stations may be required.
- Procedures need to be put in place to allow data compilation at national
level and reporting to the Commission within six months after each calendar
year.
- Procedures need to be put in place to ensure that in case the
concentrations exceed the limit values, the Commission is informed thereof and
that plans are developed for the progressive improvement of the quality of air
in those zones. This requires identification of the main sources of pollution
and an assessment of emission reduction possibilities.
Tropospheric Ozone Pollution
As ground-level ozone levels are increasing, mainly due to the increase in
motor vehicle traffic in the EU, Directive 92/72/EEC required the Member States
to establish an ozone monitoring network. It set health and vegetation
protection thresholds for ozone and required each Member State to warn the
population when these thresholds were exceeded. Threshold exceedances had to be
notified to the Commission on a monthly basis.
During the course of 1998, the Commission intends to come forward with a
proposal for a Directive within the context of the Air Quality Framework
directive, establishing limit/target values for tropospheric ozone together with
very precise monitoring requirements. When the provisions of this foreseen new
directive start to enter into force it will progressively replace the provisions
of Directive 92/72/EC.
Implementation considerations
- Countries need to assess whether there are operational measuring stations
at sites where the threshold values are likely to be exceeded. The sites need to
be selected in accordance with Annex II and need to use a reference method for
analysis in accordance with Annex V. Additional measuring stations may be
required.
- Procedures need to be put in place to ensure that in case the
concentrations exceed the limit values, the public is informed in accordance
with Annex IV, and the Commission is informed by the end of the following month.
- Procedures need to be put in place to allow data compilation at national
level and annual reporting to the Commission.
Air Quality Framework Directive - Implementation
Considerations
National Legislative Framework
- Compare directive's requirements to existing national laws and regulations
- Identify legislative gaps
- Options:
|
Competent Authorities (CAs)
- Determine CAs for legal and administrative purposes
- National level CA will report to Commission on implementation
- Identify monitoring institutions and needs
- Define planning procedures and implementation controls
- Ensure transparency of decision-making, appeals and review of decisions
- Prepare Air quality improvement plans where needed
|
Legal Checkpoints
- Ensure monitoring, compliance, enforcement and reporting procedures.
- Ensure implementation of time limits fixed for air quality limit values.
- Provide full disclosure to the public where there are air pollution
exceedances.
Air Quality Framework Directive Implementation considerations |
The Standards Process
- Follow EU development of air quality objectives for the 14 pollutants
listed in the Directive
- Be aware of timelines for the implementation of limit values which can vary
from 10 to 15 years
- Determine when concentrations are between long term limit values and
temporary tolerant values. Take action to meet long term limit values
- Monitor compliance
|
Stakeholders
- Ensure that prior to air quality law creation, all parties including local
government, affected government departments (e.g., transport), industry
representatives, and the public are given the opportunity to comment.
- Make all Air Quality laws and guidelines publicly available.
- Ensure that ambient air quality limit values become a key planning tool for
industry.
|
Financial Considerations
- Member States to provide permitting authorities, monitoring and control
- Affected industry to pay costs of compliance.
|
B.3 Emissions from Mobile Sources
Light duty motor vehicles
The base-directive 70/220/EEC lays down the technical requirements and the
limit values for carbon monoxide and unburnt hydrocarbon emissions from the
engines of motor vehicles. These requirements were made much more stringent over
the past 25 years by a series of amending directives. The limit values were
first reduced by Directive 74/290/EEC and supplemented, with Directive
77/102/EEC, by limit values for nitrogen oxides. The limit values for these
three types of pollution were successively reduced by Directives 78/665/EEC,
83/351/EEC and 88/76/EEC, whereas limit values for particulate pollutant
emissions from diesel engines were introduced by directive 88/436/EEC. More
stringent European standards for the emissions of gaseous pollutants of motor
vehicles below 1400 cm³ were introduced by Directive 89/458/EEC. These
standards have been extended by Directive 91/441/EEC to cover all passenger cars
independently of their engine capacity, including requirements relating to
evaporative emissions and to the durability of emissions-related vehicle
components as well as more stringent particulate pollutant standards for motor
vehicles equipped with diesel engines.
Directive 94/12/EC introduced more stringent limit values for all pollutants
and a modification of the control of conformity of the production. Passenger
cars designed to carry more than six passengers and having a maximum mass of
more than 2500 kg, light commercial vehicles, and such off-road vehicles, which
previously benefited from less stringent standards, have been submitted by
directive 93/59/EEC and directive 96/69/EC to standards as severe as the
respective standards for passenger cars, taking into account the specific
conditions of these vehicles.
The Auto-Oil programme
Directive 94/12/EC requires that the Commission proposes standards to be
enforced after the year 2000, according to a new multi-faceted approach, based
on a comprehensive assessment of costs and efficiency of all measures aimed at
reducing roadtransport pollution. Besides tighter car emission standards, the
proposal should include complementary measures, like an improvement in fuel
quality and a strengthening of the car fleet inspection and maintenance
programme. The proposal should be based on the establishment of air quality
criteria and associated emission reduction objectives and an evaluation of the
cost/effectiveness of each package of measures, taking into account the
potential contribution of other measures such as, inter alia, traffic
management, enhancement of urban public transport, new propulsion technologies,
or the use of alternative fuels. The necessary background investigation and
research were carried out within the European Auto-Oil Programme.
The corresponding proposal for an amending directive, COM/96/0163 (COD), on
emissions from light duty motor vehicles covered by the scope of the
base-directive 70/220/EEC, was presented in June 1996 and is presently discussed
in the European Parliament and the Council.
In parallel a proposal for a directive, COM/96/0164 (COD), laying down new
requirements to improve the quality of motor fuels was presented by the
Commission. This proposal is also under discussion in the European Parliament
and the Council. (See B.7).
However, in order to achieve the air quality criteria laid down in the
Auto-Oil programme , additional cost/effective local measures will nevertheless
be needed in the most polluting areas.
Heavy duty diesel engines for motor vehicles
Directive 88/77/EEC established emission requirements for carbon monoxide,
hydrocarbon and nitrogen oxides. Besides a strengthening of the original limits
introducing a two stage approval to be implemented in year 1993 and year 1996,
requirements for particulate emissions were set with amending directive
91/542/EEC. Amending directive 96/1/EC allowed for some derogation on the
particulate emission limit of smaller engines. In context with the approach
explained above a new proposal is currently being prepared in order to introduce
stricter requirements from the year 2000 onwards.
Emissions from engines to be installed in mobile machinery
A proposal for a new directive, COM 95/350 (COD),setting emission
requirements for carbon monoxide, hydrocarbon, nitrogen oxides and particulates
on mobile machinery diesel engines is presently under discussion in Council and
the Parliament and is expected to be adopted shortly.
Smoke emissions from diesel engines of motor vehicles, agricultural and
forestry tractors
Directives 72/306/EEC and 77/537/EEC set standards for maximum capacity of
diesel exhaust smoke. The main purpose of these standards is the establishment
of reference values for roadworthiness testing mentioned below.
Implementation considerations
- Countries will have to determine the type-approval authorities as defined
in Directive 70/156/EEC and its amendments.
- Where necessary the type-approval authorities can delegate technical work
to accredited technical services that can be situated in any Member State.
- For advice on how to establish effective administrative structures,
type-approval authorities and technical services, preferably in Member States
which have dealings with a large national automotive industry, should be
consulted.
Roadworthiness Test for Emissions Directive
Directive 77/143/EEC on road worthiness tests for motor vehicles and their
trailers, as amended by directive 92/55/EEC, requires testing vehicle emissions
in regular roadworthiness tests for the control of carbon monoxide (CO) and the
air-fuel ratio for petrol fuelled vehicles and of the opacity of the exhausts
from diesel vehicles.
Implementation considerations
1.The roadworthiness tests shall be carried out by the State, or by a public
body entrusted with the task by the State or by bodies or establishments
designated and directly supervised by the State, including duly authorized
private bodies.
2.In particular, when establishments designated as vehicle testing centres
also perform motor vehicle repairs, Member States shall make every effort to
ensure the objectivity and high quality of the vehicle testing.
3.Advice should be requested from public or entrusted bodies of those Member
States which have them in place for a long time and thus ensuring comprehensive
experience and expertise.
B.4 Volatile Organic Compounds Emissions
Directive 94/63/EC aims to control emissions of volatile organic compounds
(VOC) emissions resulting from the storage of petrol and its distribution from
terminals to service stations. It applies to the operations, installations, road
vehicles, trains and inland waterway vessels used for the storage and
transportation of petrol from one terminal to another or from a terminal to a
service station. The provisions of this directive are currently being revised.
Implementation considerations
- Countries need to establish laws, monitoring and enforcement systems for
meeting the emission limits for petrol vapour from storage tanks and mobile
containers: trucks, trains and inland waterway vessels.
- Nationally harmonised testing procedures must be applied by competent
authorities monitoring terminals and service stations, as well as vehicles and
vessels for the transport of petrol.
- Countries must implement a range of technical and management requirements
to minimise vapour losses from the handling of petrol at terminal and service
stations and during transport.
- Prior consultation with industry and other interested groups is advised.
Directive on Emissions from Motor Vehicles
Implementation Considerations
National Legislative Framework
Compare directive requirements to existing national laws.
Identify legislative gaps.
Options:
One main legislative tool (Motor Vehicle Act);
Adapt a section of the relevant legislation governing air emissions (e.g.,
Environmental Protection Act or Air Act). |
Competent Authorities (CAs)
The National Authority should assume responsibility for uniform emission
standards, overall quality assurance and tax administration issues.
Local CAs could manage local emissions monitoring and enforcement
activities.
National CA to observe reporting duties to Commission. |
Legal Checkpoints
- Develop a regulatory regime which can cope with frequent emissions
reduction measures.
- Key measures include legislative apparatus for emissions reductions, tax
incentives, new technologies, inspection and maintenance procedures.
- Consider local monitoring and enforcement measures.
|
Compliance Procedures
- Authorised CA personnel could operate national inspection centres for new
car fleets.
- CA to ensure compliance with production line vehicle emission conformity
certificates.
- Petrol stations must be spot-checked concerning fuel nozzle sizes, petrol
vapour recovery from refuelling of underground storage tanks and octane
requirements.
- Consider licensing local private technical bodies to issue individual
vehicle emissions compliance and vehicle maintenance requirement documents.
|
Stakeholders
- Ensure that prior to the development of the regime stakeholders are
consulted over emissions standards, new technologies, technical requirements and
compliance procedures.
- Stakeholder should include members of the wholesale and retail oil and gas
industry, vehicle manufacturers and retailers, other government departments
(e.g., Transport), NGOs and other affected parties.
- Regular public communications.
|
Financial Considerations
- Government to establish CA and administrative support, public
communications, information and advice to industry.
- Tax incentives to encourage innovation and to reduce emissions.
- Vehicle manufacturers and retailers to pay for compliance certificates and
inspection measures.
- Vehicle owners to pay reasonable costs of individual vehicle compliance.
|
B.5 Lead Content of Petrol
Directive 85/210/EEC on the lead content of petrol allows Member States to
reduce the permitted lead content to 0.15 g Pb/l as soon as they consider it
appropriate; they must ensure the availability and balanced distribution of
unleaded petrol having a content below 0.013 g Pb/l). The benzene content of
both leaded and unleaded petrol may not exceed 5.0%. Unleaded petrol must be
clearly labelled at the pump. Countries may prohibit the marketing of leaded
petrol which does not meet prescribed octane levels.
The provisions of this directive will be replaced from the year 2000 by the
requirements of the proposed directive on the quality of petrol and diesel fuel,
COM 96/0164 (COD), (see B.7).
Implementation considerations
- Countries must have the administrative apparatus, including sampling and
statistical interpretation methodologies, for testing lead and benzene content
levels and punishing non-compliance. To ensure consistency on a national basis,
labelling requirements should be established and administered by the Central
Authority.
- In order to achieve compliance, both local manufacturing and retail sector
monitoring of lead, benzene and octane levels in petrol as appropriate, should
be targeted. This can be supplemented with random spot testing of imports
through border checks and at the retail pump site.
- Countries should conduct discussions on implementation options with
representatives of the oil and gas sector as well as other interested parties.
B.6 Sulphur Content of Liquid Fuels
Directive 93/12/EEC relating to the sulphur content of certain liquid fuels
sets limits on the sulphur content of diesel fuel and other gas oils. Diesel
fuel is used in some motor vehicles. Gas oil, also known as light fuel oil, is
used for self-propelling vehicles, heating, industrial and marine purposes.
With regard to diesel fuel used in road vehicles the provisions of directive
93/12/EEC will be replaced by the requirements of the proposed directive, COM
96/0164 (COD), on the quality of petrol and diesel fuel (see B.7).
With regard to gasoil and heavy fuel oil, the Commission has recently made a
proposal to revise the provisions of directive 93/12/EEC.
In order to reduce sulphur dioxide pollution, particularly ground level
concentrations in urban areas, the directive imposes maximum sulphur by weight
limits for gas and diesel oils. Further reductions in sulphur by weight limits
and related emission standards for diesel engines are anticipated. (The
Commission has proposed a strategy to combat acidification of soil and water,
together with legislation to limit the sulphur content of fuel which introduce
generalised 1% ceiling on sulphur content from the start of 2000 -COM(97) 88
final). The directive does not apply to gas oil intended for further processing
or contained in the fuel tanks of vehicles crossing a frontier between an EU
Member State and a non-EU country. New limits on the sulphur content of diesel
fuel will be introduced under the Auto-Oil programme.
Implementation considerations
- Countries must have the administrative apparatus, including sampling and
statistical interpretation methodologies, for testing sulphur content levels and
enforcing the requirements.
- Representatives for the motor vehicle industry and other interested
parties should be consulted on implementation methodologies in order to avoid
compliance problems.
B.7 Proposal for a directive on the quality of Petrol and
Diesel Fuels
This proposed directive, COM 96/0164 (COD), which is scheduled to enter into
force as from 1st January 2000 lays down specifications for the quality of
petrol and diesel fuels. With regard to petrol the parameters for which
specifications are established include benzene content, sulphur content,
aromatics, oxygen content, and distillation characteristics. In the case of
diesel the parameters concerned include density, cetane number and sulphur
content. By June 1999, the Commission will bring forward proposals to establish
fuel specifications for 2005.
|