Tag Archives: Noise

Clean Sky

Clean Sky

Outline of the Community (European Union) legislation about Clean Sky

Topics

These categories group together and put in context the legislative and non-legislative initiatives which deal with the same topic.

Environment > Air pollution

Clean Sky

Document or Iniciative

Council Regulation (EC) No 71/2008 of 18 December 2007 setting up the Clean Sky Joint Undertaking.

Summary

The “Clean Sky” joint technology initiative (JTI) is part of the “Cooperation” specific programme (7th framework programme for research and technological development).

Aims

Created to run until 31 December 2017, Clean Sky aims principally to:

  • accelerate the development of clean air transport technologies;
  • guarantee effective coordination of aeronautics research on a European scale;
  • set up an innovative and competitive air transport system;
  • improve knowledge generation and use of research findings.

In terms of figures, “Clean Sky” aims to reduce CO2 emissions by 50 %, NOx by 80 % and noise pollution by 50 % by 2020.

“Integrated Technology Demonstrators” (ITD)

Six technical domains, covering all aspects of aircraft technology and known as “integrated technology demonstrators” form the structure of “Clean Sky”. They provide a framework for research operations from the experimental phase to in-flight demonstrations.

Specifically, the six ITD are:

  • the Smart Fixed Wing ITD targeting wing technologies;
  • the Green Regional Aircraft ITD (engines, energy management and new silent configurations);
  • the Green Rotorcraft ITD targeting installation of innovative blades and engines which are quieter, reduce drag, are more fuel-efficient and use environmentally-friendly flight paths;
  • the Systems for Green Operations ITD targeting equipment, architecture and thermal management;
  • the Sustainable and Green Engines ITD integrating technologies for quiet, low weight, low pressure systems and reducing nitrogen oxides (NOx);
  • the Eco-Design ITD, which will focus on the full life cycles of materials and components (design, manufacture, maintenance and destruction/recycling).

An independent technical evaluator will assess and monitor the results of research carried out in these various sectors in order to optimise the impact of the programme in terms of achieving its environmental objectives.

Members and bodies

Its founding members are:

  • the European Union (EU) represented by the Commission;
  • twelve ITD leaders and associates;
  • any public or private entity (industry, company, SME, research centre, university, etc.) established in a Member State or in a country associated with the 7th Framework Programme which, under certain conditions and subject to the consent of the governing board, may request membership.

Its bodies are:

  • the Governing Board;
  • the Executive Director;
  • the ITD Steering Committees;
  • the Technology Evaluator Steering Committee;
  • the General Forum.

A National States Representative Group will act as an external advisory body to the undertaking.

Budget

The maximum Community contribution will be EUR 800 million paid from the budget appropriation allocated to the “Transport” theme of the “Cooperation” Specific Programme. Added to this is a contribution which is at least equivalent from the other members of the undertaking, giving a total budget of EUR 1.6 billion.

General information

As a Community body, “Clean Sky” has legal status.

Further information on the objectives and activities of the “Clean Sky” JTI, its status and operation, the role and tasks of its members and bodies, and its funding, are available in the annex to the Regulation.

Background

In addition to “Clean Sky”, five other initiatives of this type are planned in the areas of miniaturisation (ENIAC), invisible information systems (ARTEMIS), innovative medicine, hydrogen and fuel cells and global monitoring for environment and security (GMES).

References

Act Entry into force – Date of expiry Deadline for transposition in the Member States Official Journal

Regulation (EC) No 71/2008

7.2.2008 – 31.12.2017

OJ L 30 of 4.2.2008

The successive amendments and corrections to Regulation (EC) No 71/2008 have been integrated into the original text. This consolidated versionis for reference only.

Noise pollution

Noise pollution

Outline of the Community (European Union) legislation about Noise pollution

Topics

These categories group together and put in context the legislative and non-legislative initiatives which deal with the same topic.

Environment > Noise pollution

Noise pollution

Noise above a certain volume threshold (from 60 Ldn dB(A) according to the European Environment Agency) affects not only wellbeing, but also the health of citizens. On top of the corrective measures applicable to some sources of noise, in 2002 the European Union adopted a Directive setting out a Community approach to the management and evaluation of ambient noise in order to protect public health.

GENERAL FRAMEWORK

  • Assessment and management of environmental noise
  • Action against noise: Green Paper

SOURCES OF NOISE POLLUTION

  • Motor vehicles with trailers: permissible sound level
  • Noise emission by equipment used outdoors
  • Noise management at EU airports

Assessment and management of environmental noise

Assessment and management of environmental noise

Outline of the Community (European Union) legislation about Assessment and management of environmental noise

Topics

These categories group together and put in context the legislative and non-legislative initiatives which deal with the same topic.

Environment > Noise pollution

Assessment and management of environmental noise

Document or Iniciative

Directive 2002/49/EC of the European Parliament and of the Council of 25 June 2002 relating to the assessment and management of environmental noise [See amending act(s)].

Summary

This Directive is aimed at controlling noise perceived by people in built-up areas, in public parks or other quiet areas in an agglomeration, in quiet areas in open country, near schools, hospitals and other noise-sensitive buildings and areas. It does not apply to noise that is caused by the exposed person him or herself, noise from domestic activities, noise created by neighbours, noise at work places or inside means of transport or noise due to military activities in military areas.

Noise indicators and their assessment methods

Lden is an indicator of the overall noise level during the day, evening and night which is used to describe the annoyance caused by exposure to noise. Lnight is an indicator for the sound level during the night used to describe sleep disturbance. The noise indicators Lden and Lnight are used in the making of strategic noise maps.

Other indicators may be used for acoustical planning and noise zoning and in the special cases as listed in Annex I to the Directive.

The values of Lden and Lnight are defined using the assessment methods set out in Annex II to the Directive. Common assessment methods for the determination of Lden and Lnight will be established by the Commission. In the meantime, Member States may use their own methods to determine the common indicators, provided that such methods conform to Annex II.

Dose-effect relations will be introduced in Annex III by future revisions in order to be able to assess the effect of noise on populations.

No later than 18 July 2005, Member States are to communicate information to the Commission on any relevant limit values in force or under preparation, expressed in terms of Lden and Lnight and, where appropriate, Lday and Levening, for road-traffic noise, air-traffic noise, rail-traffic noise and industrial noise.

Strategic noise mapping

A strategic noise map enables a global assessment to be made of noise exposure in an area due to different noise sources and overall predictions to be made for such an area. The strategic noise maps must satisfy the minimum requirements laid down in Annex IV to the Directive.

No later than 18 July 2005, Member States are to make available to the public information concerning the competent authorities and bodies responsible for making and, where relevant, approving strategic noise maps.

No later than 30 June 2005, and thereafter every five years, Member States must inform the Commission of the major roads which have more than six million vehicle passages a year, railways which have more than 60 000 train passages per year, major airports and the agglomerations with more than 250 000 inhabitants within their territories. By 30 June 2007 at the latest, strategic noise maps showing the situation during the preceding year in the vicinity of the infrastructures and in the agglomerations referred to must have been made and, where relevant, approved.

No later than 31 December 2008, Member States are to inform the Commission of all the agglomerations with more than 100 000 inhabitants and of all the major roads and major railways within their territories. By 30 June 2012 at the latest, and thereafter every five years, strategic noise maps showing the situation during the preceding year must be made and, where relevant, approved for those agglomerations, roads and railways.

Noise maps must be reviewed, and revised if necessary, every five years.

Action plans

Action plans are aimed at managing noise issues and effects, including noise reduction if necessary. They must meet the minimum requirements set out in Annex V to the Directive.

The measures within the plans are at the discretion of the competent authorities, but should address priorities which may be identified by the exceeding of any relevant limit value or by other criteria chosen by the Member States and apply in particular to the most important areas as established by strategic mapping.

No later than 18 July 2005, Member States are to make available to the public information concerning the authorities and bodies responsible for drawing up and, where relevant, approving the action plans.

No later than 18 July 2008, action plans must be drawn up for major roads which have more than six million vehicle passages a year, railways which have more than 60 000 train passages per year, major airports and agglomerations with more than 250 000 inhabitants.
No later than 18 July 2013, action plans must be drawn up for all major agglomerations, major airports, major roads and major railways.

The action plans are to be reviewed when a major development occurs affecting the existing noise situation, and at least every five years.

Information for the citizen

Member States are to ensure that a public consultation is organised and the results thereof are taken into account before the action plans are approved.

Member States are to ensure that the strategic noise maps and the action plans are made available and disseminated to the public in conformity with Annexes IV and V to this Directive and in accordance with the Directive on the freedom of access to information on the environment.

Reports concerning the Directive

On 10 March 2004, the Commission forwarded a report to the European Parliament and the Council on existing Community measures relating to sources of environmental noise (see “Related Acts” below).

Member States are to collect the noise maps and action plans. They are to forward to the Commission the information contained in the noise maps and a summary of the action plans. Every five years, the Commission is to publish a summary report on the data contained in the noise maps and action plans. The first report will be submitted by 18 July 2009.

No later than 18 July 2009, the Commission is to submit to the European Parliament and the Council a report on the application of this Directive. The report will assess the need for further Community actions on environmental noise and, if appropriate, propose implementing strategies. It is to include in particular a review of the acoustic environment quality in the Community. The report is to be reviewed every five years.

References

Act Entry into force Deadline for transposition in the Member States Official Journal

Directive 2002/49/EC

18.7.2002

18.7.2002

OJ L 189 of 18.7.2002

Amending act(s) Entry into force Deadline for transposition in the Member States Official Journal

Regulation (EC) No 1137/2008

11.12.2008

OJ L 311 of 21.11.2008

The successive amendments and corrections to Directive 2002/49/EC have been incorporated into the original text. This consolidated versionis for reference only.

Related Acts

Report from the Commission to the European Parliament and the Council of 1 June 2011 on the implementation of the Environmental Noise Directive in accordance with Article 11 of Directive 2002/49/EC [COM (2011) 321 final – Not published in the Official Journal].

Report from the Commission to the European Parliament and the Council of 10 March 2004 concerning existing Community measures relating to sources of environmental noise, pursuant to article 10(1) of Directive 2002/49/EC relating to the assessment and management of environmental noise [COM(2004) 160 – Not published in the Official Journal].

Tyre labelling

Tyre labelling

Outline of the Community (European Union) legislation about Tyre labelling

Topics

These categories group together and put in context the legislative and non-legislative initiatives which deal with the same topic.

Internal market > Motor vehicles > Technical harmonisation for motor vehicles

Tyre labelling

Document or Iniciative

Regulation (EC) No 1222/2009 of the European Parliament and of the Council of 25 November 2009 on the labelling of tyres with respect to fuel efficiency and other essential parameters (Text with EEA relevance).

Summary

This Regulation aims at harmonising information concerning the energy performance of tyres, as well as on wet braking and external rolling noise. It should promote tyres which are both energy-efficient and capable of braking on wet roads, and which also increase the energy efficiency and safety of road transport. The inclusion of noise should also encourage consumers to buy low noise tyres and therefore reduce traffic noise.

It applies to C1, C2 and C3 * tyres and excludes from its scope:

  • re-treaded tyres;
  • off-road professional tyres;
  • tyres designed to be fitted only to vehicles registered for the first time before 1 October 1990;
  • T-type temporary-use spare tyres *;
  • tyres whose speed rating is less than 80 km/h;
  • tyres whose nominal rim diameter does not exceed 254 mm or is 635 mm or more;
  • tyres fitted with additional devices to improve traction properties (for example studded tyres);
  • tyres designed only to be fitted on vehicles intended exclusively for racing.

Responsibilities of tyre suppliers *

Tyre suppliers must monitor the labelling of C1, C2 and C3 tyres delivered to distributors and end-users.

This labelling includes a sticker which must indicate:

  • the fuel efficiency class (letter A to G);
  • the wet grip class (letter A to G); at this stage the Regulation only provides classification for wet grip performance for C1 tyres, but intends to introduce a classification for C2 tyres and eventually C3 tyres once tests are available;
  • the external rolling noise measured value (in decibels).

Suppliers must declare this information in the technical promotional literature * for tyres such as on their website or in catalogues.

Responsibilities of tyre distributors *

Distributors must ensure that the labels delivered by suppliers are clearly visible on the tyres presented or stored at the point of sale. If tyres cannot be seen by end-users, they must supply this information to users themselves.

Responsibilities of car suppliers and car distributors

If end-users of vehicles can choose their tyres, car suppliers and car distributors must give them the performance of each option of tyre in terms of fuel efficiency, wet braking and rolling noise.

Context

Tyres are responsible for 20 to 30 % of vehicles’ fuel consumption. The purchase of good quality tyres therefore allows fuel consumption to be reduced considerably and consequently less CO2 to be produced. This is why labelling presenting detailed information on tyres is of prime importance for the protection of the environment.

This Regulation is part of the Lisbon Strategy and the strategy for sustainable development. It will contribute to reducing the carbon footprint of road transport, and therefore reaching the goals fixed in terms of sustainable mobility.

Key terms of the Act
  • C1, C2 and C3 tyres: see the definition in Article 8 of COM(2008) 316. These categories include tyres mounted on passenger vehicles and light and heavy-weight commercial vehicles.
  • T-type temporary-use spare tyres: temporary-use spare tyre designed for use at inflation pressures higher than those established for standard and reinforced tyres.
  • Technical promotional literature: all printed and electronic material used in the marketing of tyres or vehicles aimed at end-users or distributors which describes the specific parameters of a tyre, including technical manuals, brochures, Internet marketing, leaflets and catalogues;
  • Supplier: the manufacturer or its authorised representative in the Community or the importer.
  • Distributor: any natural or legal person in the supply chain, other than the supplier or the importer, who makes a tyre available on the market.
  • End-user: a consumer, including a fleet manager or road transport company that is buying or expected to buy a tyre.

References

Act Entry into force Deadline for transposition in the Member States Official Journal

Regulation No 1222/2009

11.10.2010

OJ L 342 of 22.12.2009

Noise emission by equipment used outdoors

Noise emission by equipment used outdoors

Outline of the Community (European Union) legislation about Noise emission by equipment used outdoors

Topics

These categories group together and put in context the legislative and non-legislative initiatives which deal with the same topic.

Environment > Noise pollution

Noise emission by equipment used outdoors

Document or Iniciative

Directive 2000/14/EC of the European Parliament and of the Council of 8 May 2000 on the approximation of the laws of the Member States relating to the noise emission in the environment by equipment for use outdoors [See amending acts].

Summary

This framework Directive harmonises the 9 existing legal instruments on noise emissions for each type of construction plant and equipment, as well as a directive on lawnmowers. The aim is to improve the control of noise emissions by more than 50 types of equipment used outdoors, such as compressors, excavator-loaders, different types of saws, mixers, etc. (Annex I).

The aim of the Directive is to promote the smooth functioning of the internal market and to improve the health and well-being of the population by reducing the noise emitted by equipment used outdoors. With a view to achieving this aim, it provides for four types of action:

  • harmonisation of noise emission standards;
  • harmonisation of conformity assessment procedures;
  • harmonisation of noise level marking;
  • gathering of data on noise emissions.

The following equipment is excluded:

  • non-powered attachments that are separately placed on the market or put into service (except for hand-held concrete-breakers and picks);
  • all equipment intended for the transport of goods or persons by public road or rail or by air or on waterways;
  • equipment designed and constructed for use by the police or the military.

Member States will be responsible for verifying that the Directive’s provisions are being applied. Annex V contains the various checking procedures to be employed.

The manufacturer or the person placing the equipment on the market or putting it into service must ensure (Annex V, 2) that:

  • they have drawn up a declaration of conformity certifying that each of item of equipment is in conformity with the provisions of the Directive;
  • they have affixed an indelible legible marking to each item of equipment indicating the guaranteed sound power level.

Where a Member State ascertains that equipment does not comply with these conditions, it must withdraw it from the market or prohibit its use.

Labelling is compulsory for all items of equipment covered by the Directive and must include:

  • the CE marking visibly, legibly and indelibly affixed to each item of equipment;
  • details of the sound power level Lwa in dB(A) in relation to 1 pW.

The noise emission limits * laid down for certain types of equipment involve two stages, so as to enable undertakings to adapt to the new regulations. The emission limits for stage 1 take effect two years after the entry into force of the Directive. More stringent limits will enter into force in stage 2 four years later.

Responsibility for monitoring the noise emission limits applicable to the equipment is vested in a notified body set up by the Member States. These monitoring controls apply both to the equipment design phase and the equipment production phase. On the other hand, it is not necessary to monitor the design of equipment that is subject only to compulsory marking.

With a view to assessing the impact of the Directive, a procedure for the collection of noise emission data will be established. This information will serve as the basis for devising economic incentives and eco-label awards. Responsibility for collecting the data will rest with the certification bodies, which will be required to send the Commission a copy of their test reports. The Commission envisages the appointment of the European Environmental Agency to collect and evaluate these data.

The document has ten annexes on the following subjects:

  • definitions of equipment;
  • EC declaration of conformity;
  • method of measurement of airborne noise emitted by equipment for use outdoors;
  • models of the CE marking of conformity and of the indication of the guaranteed sound power level;
  • internal control of production;
  • internal control of production with assessment of technical documentation and periodical checking;
  • unit verification;
  • full quality assurance;
  • minimum criteria to be taken into account by Member States for the notification of bodies;
  • unit verification – model of conformity certificate.

Background

The Commission Green Paper of 1996 on Noise Policy highlighted the increase of noise pollution in urban areas. Some 20 % of the population of Western Europe have to endure noise levels judged by the experts as unacceptable. While most external noise is caused by transport equipment, the extent of noise emissions as the result of the use of outdoor equipment is constantly increasing.

Termes clés
  • Noise limits are laid down following a general formula: L = A + B 1g P, where
    1. L is the sound emission limit,
    2. P is a power-related descriptor,
    3. A and B are product-related constants.

References

Act Entry into force Deadline for transposition in the Member States Official Journal

Directive 2000/14/EC

3.7.2000

3.7.2001

OJ L 162 of 3.7.2000

Amending act(s) Entry into force Deadline for transposition in the Member States Official Journal

Directive 2005/88/EC

27.12.2005

31.12.2005

OJ L 344 of 27.12.2005

Regulation (EC) No 219/2009

20.4.2009

OJ L 87 of 31.3.2009

Successive amendments and corrections to Directive 2000/14/EC have been incorporated in the basic text. This consolidated version  is for reference purpose only.

Related Acts

Commission Recommendation of 6 August 2003 concerning the guidelines on the revised interim computation methods for industrial noise, aircraft noise, road traffic noise and railway noise, and related emission data [C(2003) 2807 – Official Journal L 212 of 22.08.2003].

The Commission recommends the interim application of the ISO 9613-2 engineering method for calculating the abatement of sound during propagation outdoors, in order to predict environmental noise levels around a variety of sources, particularly industrial sources.

Directive 2002/49/EC of the European Parliament and of the Council of 25 June 2002 relating to the assessment and management of environmental noise – Declaration by the Commission in the Conciliation Committee on the Directive relating to the assessment and management of environmental noise [Official Journal L 189 of 18.07.2002].

Exposure to noise

Exposure to noise

Outline of the Community (European Union) legislation about Exposure to noise

Topics

These categories group together and put in context the legislative and non-legislative initiatives which deal with the same topic.

Employment and social policy > Health hygiene and safety at work

Exposure to noise

Document or Iniciative

Directive 2003/10/EC of the European Parliament and of the Council of 6 February 2003 on the minimum health and safety requirements regarding the exposure of workers to the risks arising from physical agents (noise)

Seventeenth individual Directive within the meaning of Article 16(1) of Directive 89/391/EEC [See amending acts].

Summary

EXPOSURE LIMIT VALUES AND EXPOSURE ACTION VALUES

The physical parameters used to measure noise are as follows: peak sound pressure (maximum value of instantaneous noise pressure), daily noise exposure level and weekly noise exposure level.
The exposure limit value is fixed at 87 decibels (taking into account the attenuation provided by the individual hearing protectors worn by the workers) and the exposure action values are fixed at 80 decibels (lower value) and 85 decibels (upper value).

OBLIGATIONS OF EMPLOYERS

Determination and assessment of risks

In carrying out the obligations laid down in the framework Directive on the improvement of the health of workers at work, the employer, via the intermediary of the competent services, must assess and, if necessary, measure the levels of noise to which workers are exposed. The results of this assessment must be recorded on a suitable medium and kept up to date on a regular basis.

The employer must give particular attention, when carrying out the risk assessment, to the following:

  • the level, type and duration of exposure, including any exposure to impulsive noise;
  • the exposure limit values and the exposure action values;
  • any effects concerning the health and safety of workers belonging to particularly sensitive risk groups;
  • as far as technically achievable, any effects on workers’ health and safety resulting from interactions between noise and work-related ototoxic substances, and between noise and vibrations;
  • any indirect effects on workers’ health and safety resulting from interactions between noise and warning signals or other sounds;
  • information on noise emission provided by manufacturers of work equipment in accordance with the relevant Community directives;
  • the existence of alternative work equipment designed to reduce the noise emission;
  • the extension of exposure to noise beyond normal working hours under the employer’s responsibility;
  • appropriate information obtained following health surveillance;
  • the availability of hearing protectors with adequate attenuation characteristics.

Provisions aimed at avoiding or reducing exposure

Taking account of technical progress and of the availability of measures to control the risk at source, the risks arising from exposure to noise must be eliminated at their source or reduced to a minimum. The reduction of the basic risks must be based on the general principles of prevention set out in Directive 89/391/EEC and take into account in particular:

  • other working methods that require less exposure to noise;
  • the choice of appropriate work equipment;
  • the design and layout of workplaces and work stations;
  • adequate information and training to instruct workers to use work equipment correctly in order to reduce their exposure to noise to a minimum;
  • noise reduction by technical methods: reducing airborne noise (shields, enclosures, sound-absorbant coverings) and reducing structure-borne noise (dampening, isolation);
  • appropriate maintenance programmes for work equipment, the work place and workplace systems;
  • organisation of work to reduce noise: limitation of the duration and intensity of exposure and appropriate work schedules with adequate rest periods.

Workplaces where workers are likely to be exposed to noise exceeding the exposure action values should be marked with appropriate signs and access to them should be restricted.

Where, owing to the nature of the activity, a worker benefits from the use of rest facilities under the responsibility of the employer, noise in these facilities must be reduced to a level compatible with their purpose and the conditions of use.

Personal protection

If the risks arising from exposure to noise cannot be prevented by other means, properly fitting individual hearing protectors must be made available to workers and used by them in accordance with Directive 89/656/EEC on the use of personal protective equipment:

  • where noise exposure exceeds the lower exposure action values, the employer must make individual hearing protectors available to workers;
  • where noise exposure matches or exceeds the upper exposure action values, individual hearing protectors must be used;
  • the individual hearing protectors must be so selected as to eliminate the risk to hearing or to reduce the risk to a minimum.

Limitation of exposure

Under no circumstances may the exposure of the worker exceed the exposure limit values. If, despite the measures taken to implement this Directive, exposures above the exposure limit values are detected, the employer must:

  • take immediate action to reduce the exposure to below the exposure limit values,
  • identify the reasons why overexposure has occurred and amend the protection and prevention measures in order to avoid any recurrence.

Worker information and training

The employer must ensure that workers who are exposed to noise at work at or above the lower exposure action values, and/or their representatives, receive information and training relating to risks resulting from exposure to noise concerning, in particular:

  • the nature of such risks;
  • the measures taken to implement this Directive in order to eliminate or reduce to a minimum the risks from noise, including the circumstances in which the measures apply;
  • the exposure limit values and the exposure action values;
  • the results of the assessment and measurement of the noise carried out, together with an explanation of their significance and potential risks;
  • the correct use of hearing protectors;
  • why and how to detect and report signs of hearing damage;
  • the circumstances in which workers are entitled to health surveillance and the purpose of health surveillance;
  • safe working practices to minimise exposure to noise.

Consultation and participation of workers

Consultation and participation of workers and/or of their representatives must take place on the matters covered by this Directive, in particular:

  • the assessment of risks and identification of measures to be taken;
  • the actions aimed at eliminating or reducing risks arising from exposure to noise;
  • the choice of individual hearing protectors.

MISCELLANEOUS PROVISIONS

Health surveillance

When the noise levels present a health risk, Member States must adopt provisions to ensure the appropriate health surveillance of workers (preservation of the hearing function):

  • workers whose exposure exceeds the upper exposure action values have the right to have their hearing checked;
  • workers whose exposure to noise exceed the lower exposure action values have the right to preventive audiometric testing.

Member States must establish arrangements to ensure that individual health records are made and kept up to date for these workers. These records may be consulted at a later date and are accessible to the workers concerned.

Where, as a result of surveillance of the hearing function, a worker is found to have an identifiable hearing damage, a doctor shall assess whether the damage is likely to be the result of exposure to noise at work. If this is the case:

  • the worker must be informed by the doctor or other suitably qualified person of the result which relates to him or her personally.
  • the employer must review the risk assessment;
  • the employer must review the measures provided for to eliminate or reduce risks;
  • the employer must take into account the advice of the occupational health-care professional or other suitably qualified person in implementing any measures required to eliminate or reduce risk, including the possibility of assigning the worker to alternative work where there is no risk of further exposure;
  • the employer must arrange continued health surveillance and provide for a review of the health status of any other worker who has been similarly exposed.

Derogations

In exceptional situations where, because of the nature of the work, the full and proper use of individual hearing protectors would be likely to cause greater risk to health or safety than not using such protectors, Member States may grant derogations from the provisions concerning personal protection and limitation of exposure.

Such derogations must be reviewed every four years and withdrawn as soon as the justifying circumstances no longer obtain.

Code of conduct

In the music and entertainment sectors, Member States may have recourse to a transitional period of up to a maximum of two years to prepare a code of conduct providing for practical guidelines to help workers and employers in these sectors to meet their legal obligations as laid down in this Directive.

Reporting

Every five years Member States must provide a report to the Commission on the practical implementation of this Directive. On the basis of those reports, the Commission shall carry out an overall assessment.

References

Act

Entry into force

Deadline for transposition in the Member States

Official Journal

Directive 2003/10/EC

15.02.2003

15.02.2006
For the music and entertainment sector: 15.02.2008
For personnel on board seagoing vessels: 15.02.2011

OJ L 42 of 15.02.2003

Amending act(s)

Entry into force

Deadline for transposition in the Member States

Official Journal

Directive 2007/30/EC

28.6.2007

31.12.2012

OJ L 165 of 27.6.2007