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S.I. No. 140 of 2006
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Environmental Noise Regulations 2006
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The Minister for the Environment, Heritage
and Local Government, in exercise of the powers conferred on him by sections
6, 53 and 106 of the Environmental Protection Agency Act 1992 (No. 7 of
1992), as amended by Part 2 of the Protection of the Environment Act 2003
(No. 27 of 2003), for the purpose of giving effect to Council Directive
2002/49/EC relating to the assessment and management of environmental noise
(1 ) hereby makes the
following Regulations: -
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Citation
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1 These Regulations
may be cited as the Environmental Noise Regulations 2006.
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Entry into Force
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2 These Regulations
shall come into operation on the 3rd day of April 2006.
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Interpretation
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3 (1) In
these Regulations, unless the context otherwise requires:-
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“acoustical planning” means controlling future noise by planned
measures, such as land-use planning, systems engineering for traffic,
traffic planning, abatement by sound-insulation measures and control of
noise sources;
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“the Act” means the Environmental Protection Agency Act 1992 ;
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“action plan” means a plan designed for the purpose of managing
noise issues and their effects, including noise reduction if necessary;
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“action planning authority” has the meaning assigned by article 7;
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“the Agency” means the Environmental Protection Agency established
under Section 19 of the Environmental Protection Agency Act 1992 (No. 7 of
1992);
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“agglomeration of Cork” means the restricted area of Cork as
specified in the First Schedule to the Air Pollution Act 1987 (Marketing,
Sale and Distribution of Fuels) Regulations 1998 ( S.I. No. 118 of 1998 );
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“agglomeration of Dublin” means the county borough of Dublin, the
administrative county of Dun Laoghaire/Rathdown
other than those areas excluded in the First Schedule to the Air Pollution
Act 1987 (Marketing, Sale and Distribution of Fuels) Regulations 1998 ( S.I.
No. 118 of 1998 ), and the administrative counties of Fingal
and South Dublin;
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“airport authority” means an airport authority established under
Section 6 of the State Airports Act (No. 32 of 2004);
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“the Commission” means the Commission of the European Communities;
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“the Directive” means Council Directive 2002/49/EC relating to the
assessment and management of environmental noise;
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“environmental noise” means unwanted or harmful outdoor sound
created by human activities, including noise emitted by means of transport,
road traffic, rail traffic, air traffic, and from sites of industrial
activity including those defined in Annex I to Council Directive 96/61/EC of
24 September 1996 concerning integrated pollution prevent and control (2
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“larnród Éireann”
means the company charged with the management, operation and development of
Ireland's rail network under the Transport (Re-organisation of Coras lompair Éireann) Act 1986 (No. 31 of 1986);
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“Lden” (day-evening-night noise
indicator) means the noise indicator for overall annoyance, as further
defined in the First Schedule;
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“Lday” (day-noise indicator)
means the noise indicator for annoyance during the day period, as further
defined in the First Schedule;
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“Levening” (evening-noise
indicator) means the noise indicator for annoyance during the evening
period, as further defined in the First Schedule;
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“Lnight” (night-time noise
indicator) means the noise indicator for sleep disturbance, as further
defined in the First Schedule;
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“major road” means a national, regional or international road which
has more than three million vehicle passages per year;
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“major railway” means a railway line which has more than 30,000
train passages per year;
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“major airport” means a civil airport which has more than 50,000
movements per year, excluding those movements purely for training purposes
on light aircraft; in this context, “a movement” means a single take-off or
landing of an aircraft;
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“the Minister” means the Minister for the Environment, Heritage and
Local Government;
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“national authority” has the meaning assigned by article 5;
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“National Roads Authority” means the body established under Section
16 of the Roads Act 1993 (No. 14 of 1993);
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“noise-mapping” shall mean the presentation of data on an existing
or predicted noise situation in terms of a noise indicator, indicating
breaches of any relevant limit value in force, the number of people affected
in a certain area, or the number of dwellings exposed to certain values of a
noise indicator in a certain area;
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“noise-mapping body” has the meaning assigned by article 6;
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“quiet area in an agglomeration” means an area, delimited by an
action planning authority following consultation with the Agency and
approval by the Minister, where particular requirements on exposure to
environmental noise shall apply;
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“quiet area in open country” means an area, delimited by an action
planning authority following consultation with the Agency and approval by
the Minister, that is undisturbed by noise from traffic, industry or
recreational activities;
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“Railway Procurement Agency” means the body established under Section
9 of the Transport (Railway Infrastructure) Act 2001 (No. 55 of 2001);
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“road authority” has the meaning assigned by the Roads Act 1993 (No.
14 of 1993), as amended by the Local Government Act 2001 (No. 37 of 2001);
and
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“strategic noise map” means a map designed for the assessment of
noise exposure in a given area.
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(2) In these Regulations:-
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(a) any reference to an article or
sub-article which is not otherwise identified is a reference to an article
or sub-article of these Regulations;
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(b) a reference to a schedule which
is not otherwise identified is a reference to a schedule of these Regulations;
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(c) a letter, word, phrase or symbol
which has been assigned a meaning by the Directive, or is used in the
Directive, has that meaning where the context requires except where
otherwise indicated; and
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(d) a reference to a standard shall
mean the use or application of the most recent revision of that standard.
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Objective and Scope
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4 (1) These Regulations
provide for the implementation in Ireland of a common approach within the
European Community intended to avoid, prevent or reduce on a prioritised
basis the harmful effects, including annoyance, due to exposure to
environmental noise.
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(2) These Regulations shall apply to
environmental noise to which people are exposed, in particular in built up
areas, in public parks or other quiet areas in an agglomeration, in quiet
areas in open country, near schools, near hospitals, and near other noise-sensitive
buildings and areas.
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(3) These Regulations shall not apply to noise
caused by an exposed person, noise from domestic activities, noise created
by neighbours, noise at work places, noise inside means of transport, or
noise due to military activities in military areas.
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National Authority
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5 (1) The Environmental
Protection Agency shall be the designated national authority for the
purposes of these Regulations.
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(2) The Agency shall exercise
general supervision over the functions and actions of noise-mapping bodies
and action planning authorities, and provide guidance or advice to such
bodies and authorities, where necessary.
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(3) For the purposes of these Regulations, the
powers conferred on the Agency by section 63 of the Act in relation to local
authorities shall be exercisable by the Agency in relation to all bodies to
whom noise-mapping functions are assigned in article 6.
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(4) The Agency shall submit to the Commission
the information required in accordance with Article 10(2) of the Directive.
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Noise-Mapping Bodies
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6 The
following shall be designated noise-mapping bodies for the purpose of making
and approving strategic noise maps: -
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(a) for the agglomeration of
Cork, Cork City Council and Cork County Council;
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(b) for the agglomeration of
Dublin, Dublin City Council and the County Councils of Dun Laoghaire/Rathdown, Fingal,
and South Dublin;
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(c) for major railways, larnród Éireann or the Railway
Procurement Agency, as appropriate, on behalf of the action planning
authority or authorities concerned;
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(d) for
major roads:-
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(i) where
such roads are classified as national roads in accordance with Section 10 of
the Roads Act 1993 (No. 14 of 1993), the National Roads Authority, on behalf
of the action planning authority or authorities concerned, and
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(ii) other than those provided for in
sub-paragraph (i), the relevant road authority or
authorities, as appropriate; and
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(e) for major airports, the
relevant airport authority, on behalf of the action planning authority or
authorities concerned.
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Action Planning Authorities
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7 The
following shall be designated action planning authorities for the purpose of
making and approving action plans, in consultation with the Agency and the
noise-mapping body for the noise-map involved: -
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(a) for the
agglomeration of Cork, Cork City Council and Cork County Council;
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(b) for the
agglomeration of Dublin, Dublin City Council and the County Councils of Dun Laoghaire/Rathdown, Fingal,
and South Dublin;
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(c) for major
railways, the local authority or local authorities within whose functional
area or areas the railway is located;
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(d) for major
roads, the relevant local authority or local authorities within whose
functional area or areas the road is located; and
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(e) for major
airports, the local authority or local authorities within whose functional
area the airport is located.
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Noise Indicators
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8 (1) The noise
indicators Lden and Lnight,
as set out respectively in Parts I and II of the First Schedule, shall be
used by noise-mapping bodies for the preparation or revision of strategic
noise maps in accordance with article 10.
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(2) (a) Pending provision for common
assessment methods for the determination of Lden
and Lnight, as foreseen by Article 5(1)
of the Directive, noise indicators and related data used by a noise-mapping
body shall be subject to prior approval by the Agency.
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(b) Data approved by the Agency under paragraph
(a) shall be not more than three years old and shall be converted into Lden and Lnight.
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(3) Supplementary noise indicators may be used
in special circumstances, such as those set out in Part III of the First
Schedule, subject to approval by the Agency.
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(4) The Agency shall, as soon as possible after
the coming into operation of these Regulations, submit to the Commission the
information required in accordance with Article 5(4) of the Directive.
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Assessment Methods
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9 Pending adoption of
common assessment methods for the determination of Lden
and Lnight, as foreseen by Article 6(2)
of the Directive, noise-mapping bodies shall use the assessment methods
recommended in Part II of the Second Schedule.
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Strategic Noise Maps
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10 (1) The noise-mapping body or
bodies concerned shall, no later than 30 June 2007, make a strategic noise
map for each of the following areas, in respect of the calendar year 2006:-
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(a) the agglomeration of Dublin;
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(b) a major road which has more than
6 million vehicle passages per year;
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(c) a major railway which has more
than 60,000 train passages per year; and
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(d) a major airport.
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(2) Without prejudice to sub-article (1), the
noise-mapping body or bodies concerned shall, no later than 30 June 2012,
make a strategic noise map or revised map, as appropriate, for each of the
following areas, in respect of the calendar year 2011:-
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(a) an agglomeration with more than
100,000 inhabitants;
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(b) a major road; and
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(c) a major railway.
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(3) Strategic noise maps shall satisfy the
minimum requirements set out in the Third Schedule.
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(4) Noise-mapping bodies shall
co-operate, as appropriate, with their counterparts in neighbouring Member
States of the European Communities with regard to the strategic noise
mapping of border areas.
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(5) A noise map shall be reviewed by the
noise-mapping body and, if necessary, revised not later than five years
after the date on which it was made, or earlier where requested by the
Agency.
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(6) Noise-mapping bodies shall ensure that
information required for the purpose of article 5(4) is sent to the Agency
no later than one month after the date on which a map or revised map is
made.
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Action Plans
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11 (1) The action planning authority
or authorities concerned shall, no later than 18 July 2008, following
consultation with the Agency, make an action plan for each of the following
areas:-
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(a) the agglomeration of Dublin;
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(b) places near a major road which
has more than 6 million vehicle passages per year;
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(c) places near a major railway which
has more than 60,000 train passages per year; and
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(d) places near a major airport.
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(2) Without prejudice to sub-article (1), the
action planning authority or authorities concerned shall, no later than 18
July 2013, following consultation with the Agency, make an action plan or
revised action plan, as appropriate, for each of the following areas:-
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(a) an agglomeration with more than
100,000 inhabitants;
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(b) places near a major road, and
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(c) places near a major railway.
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(3) (a) Subject to prior consultation
with the Agency and to paragraph (b), the action planning authority or
authorities concerned, as the case may be, shall determine the measures to
be included in an action plan.
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(b) Each action plan shall address
priorities which:-
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(i) may be
identified on the basis of exceedances of any
relevant noise limit value or other relevant criteria established by the
Agency in accordance with sub-article 4, and
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(ii) shall, in the first instance,
address the most important area or areas, as the case may be, established by
strategic noise mapping.
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(4) Without prejudice to any relevant statutory
limit value for noise, the Agency may, following consultation with noise-mapping
bodies and action planning authorities, establish other relevant criteria
for action plan priorities for road-traffic noise, rail-traffic noise,
aircraft noise around airports and noise on industrial activity sites, and
shall, no later than 18 July 2013, inform the Minister, the Minister of
Transport and the Commission of such criteria.
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(5) Action plans shall:
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(a) satisfy the minimum requirements
set out in the Fourth Schedule.
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(b) aim to protect quiet areas.
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(6) Action planning authorities shall ensure
that:-
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(a) the public
are consulted on proposals for action plans;
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(b) the public
are given early and effective opportunities to participate in the
preparation and review of action plans;
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(c) the results
of public participation are taken into account in finalising action plans or
reviews of action plans;
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(d) the public
are informed of the decisions taken in relation to action plans;
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(e) reasonable time-frames are
adopted to allow sufficient time for each stage of public participation.
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(7) (a) Action planning authorities
shall be responsible for the review and, where necessary, revision of action
plans.
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(b) An action plan shall be reviewed
and, if necessary, revised:
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(i) in the
event of a material change in environmental noise in the area concerned,
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(ii) if requested by the Agency, or
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(iii) not later than five years after
the date on which it was made or last reviewed.
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(8) Action planning authorities shall
co-operate, as appropriate, with their counterparts in neighbouring Member
States of the European Communities with regard to the drawing up and
approval of action plans for border areas.
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(9) Action planning authorities shall ensure
that, for the purpose of article 5(4), a summary of each action plan or
revised action plan is sent to the Agency no later than one month after the
date on which the action plan or revised action plan, as the case may be,
was made.
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Access to Information
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12 (1) Noise mapping bodies and
action planning authorities shall, in accordance with the provisions of the European Communities
Act 1972 (Access to Information on the Environment) Regulations 1998 ( S.I. No. 125 of 1998 ), make
strategic noise maps and action plans available to the public and
disseminate them by any appropriate means, including through the use of
available information technologies.
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(2) Information for the public on noise maps and
action plans shall be clear, comprehensive and accessible, and shall include
a summary of the most important points.
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(3) Strategic noise-maps and
action plans shall be made available to the public no later than one month
after the date on which they are made.
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Reporting
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13 (1) The Agency, following
consultation with noise-mapping bodies, action planning authorities and the
Minister, shall:-
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(a) as soon as possible after the
coming into operation of these Regulations, and
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(b) on 30th June 2010 and
at five year intervals thereafter,
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inform the Commission of all agglomerations with more than 250,000
inhabitants, all major roads which have more than 6 million vehicle passages
per year, all major railways which have more than 60,000 train passages per
year, and all major airports within the territory of the State.
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(2) The Agency, following consultation with
noise-mapping bodies, action planning authorities and the Minister, shall,
no later than 31 December 2008, inform the Commission of all agglomerations,
all major roads and all major railways within the territory of the State.
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FIRST SCHEDULE
NOISE
INDICATORS
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Part I
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Definition of the day-evening-night level Lden.
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The day-evening-night level Lden in decibels (dB) is defined by the
following formula:
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in which:
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- Lday
is the A-weighted long-term average sound level as defined in ISO 1996-2:
1987, determined over all the day periods of a year,
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- Levening
is the A-weighted long-term average sound level as defined in ISO 1996-2:
1987, determined over all the evening periods of a year,
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- Lnight
is the A-weighted long-term average sound level as defined in ISO 1996-2:
1987, determined over all the night periods of a year;
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in which:
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- the day is 12 hours,
the evening four hours and the night eight hours. The Agency may decide to
shorten the evening period by one or two hours, and lengthen the day and/or
the night period accordingly, provided its decision is the same for all
noise sources; the Agency shall provide the Commission with information on
any systematic difference from the default option,
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- the Agency shall decide
the start of the day, and consequently the start of the evening and the
start of the night; the respective default values shall be 07.00, 19.00 and
23.00 local time. The Agency's decision shall be the same for all noise
sources;
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- a year is a relevant
year as regards the emission of sound and an average year as regards the
meteorological circumstances;
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and in which:
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- the incident sound is
considered, which means that no account is taken of the sound that is
reflected at the facade of the building under consideration (as a general
rule, this implies a 3 dB correction in case of measurement).
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The height of the Lden
assessment point depends on the application:
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- in the case of
computation for the purpose of strategic noise mapping in relation to noise
exposure in and near buildings, the assessment points must be 4,0 ± 0,2 m
(3,8 to 4,2 m) above the ground and at the most exposed facade; for this
purpose, the most exposed facade will be the external wall facing onto and
nearest to the specific noise source; for other purposes other choices may
be made,
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- in the case of
measurement for the purpose of strategic noise mapping in relation to noise
exposure in and near buildings, other heights may be chosen, but they must
never be less than 1,5 m above the ground, and results should be corrected
in accordance with an equivalent height of 4 m,
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- for other purposes such
as acoustical planning and noise zoning other heights may be chosen, but
they must never be less than 1,5 m above the ground, for example for:
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- rural areas with
one-storey houses,
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- the design of local
measures meant to reduce the noise impact on specific buildings,
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- the detailed noise
mapping of a limited area, showing the noise exposure of individual
buildings.
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Part II
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Definition of the night-time noise
indicator
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The night-time noise indicator Lnight is the A-weighted long-term average
sound level as defined in ISO 1996-2: 1987, determined over all the night
periods of a year;
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in which:
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- the night is eight
hours as defined in Part 1,
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- a year is a relevant
year as regards the emission of sound and an average year as regards the
meteorological circumstances, as defined in Part 1,
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- the incident sound is
considered, as laid down in Part 1,
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- the assessment point is
the same as for Lden.
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Part III
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Supplementary noise indicators
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In some cases, in addition to Lden and Lnight,
and where appropriate Lday and Levening, it may be advantageous to use
special noise indicators. Some examples are:
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- the noise source under
consideration operates only for a small proportion of the time (for example,
less than 20 % of the time over the total of the day periods in a year, the
total of the evening periods in a year, or the total of the night periods in
a year),
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- the average number of
noise events in one or more of the periods is very low (for example, less
than one noise event an hour; a noise event could be defined as a noise that
lasts less than five minutes; examples are the noise from a passing train or
a passing aircraft),
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- the low-frequency
content of the noise is strong,
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- LAmax,
or SEL (sound exposure level) for night period
protection in the case of noise peaks,
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- extra protection at the
weekend or a specific part of the year,
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- extra protection of the
day period,
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- extra protection of the
evening period,
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- a combination of noises
from different sources,
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- quiet areas in open
country,
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- the noise contains
strong tonal components,
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- the noise has an
impulsive character.
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SECOND
SCHEDULE
ASSESSMENT METHODS FOR THE NOISE
INDICATORS
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Part I
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Introduction
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The values of Lden
and Lnight can be determined either by
modelling or by measurement (at the assessment position). For predictions
only computation is applicable.
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Provisional computation and measurement
methods are set out in Parts II and III.
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Part II
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Recommended Interim computation methods for Lden
and Lnight
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The following methods are recommended:
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For INDUSTRIAL NOISE: ISO 9613-2: ‘Acoustics
— Abatement of sound propagation outdoors, Part 2: General method of
calculation’.
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Suitable noise-emission data (input data) for
this method can be obtained from measurements carried out in accordance with
one of the following methods:
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- ISO 8297: 1994
‘Acoustics — Determination of sound power levels of multisource
industrial plants for evaluation of sound pressure levels in the environment
— Engineering method’,
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- EN ISO 3744: 1995
‘Acoustics — Determination of sound power levels of noise using sound
pressure — Engineering method in an essentially free field over a reflecting
plane’,
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- EN ISO 3746: 1995
‘Acoustics — Determination of sound power levels of noise sources using an
enveloping measurement surface over a reflecting plane’.
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For AIRCRAFT NOISE: ECAC.CEAC
Doc. 29 ‘Report on Standard Method of Computing Noise Contours around Civil
Airports’, 1997. Of the different approaches to the modelling of flight
paths, the segmentation technique referred to in section 7.5 of ECAC.CEAC Doc. 29 will be used.
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For ROAD TRAFFIC NOISE one of the following
methods is recommended:
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- the UK national
computation method ‘Calculation of Road Traffic Noise (CRTN),
Department of Transport - Welsh Office, HMSO, London, 1988. This method shall
be adapted as set out in paragraph 2.1 of Annex II to the Directive.
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- the French national
computation method ‘NMPB-Routes-96 (SETRA-CERTU-LCPCCSTB)’,
referred to in ‘Arrêté du
5 mai 1995 relatif au
bruit des infrastructures routières, Journal Officiel du 10 mai 1995, Article 6’ and in the French standard ‘XPS 31-133’. For input data concerning emission, these
documents refer to the ‘Guide du bruit des
transports terrestres, fascicule prévision des niveaux sonores, CETUR 1980’.
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For RAILWAY NOISE one of the following
methods is recommended:
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- the UK national
computation method ‘Calculation of Rail Noise (CRN),
Department of Transport, HMSO, London, 1995. This method shall be adapted as
set out in paragraph 2.1 of Annex II to the Directive.
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- the Netherlands
national computation method published in ‘Reken-
en Meetvoorschrift Railverkeerslawaai
‘96, Ministerie Volkshuisvesting,
Ruimtelijke Ordening en Milieubeheer, 20 November 1996’.
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These methods must be adapted to the
definitions of Lden and Lnight.
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Part III
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Interim measurement methods for Lden and Lnight
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The measurement method may be defined on the
basis of the definition of the indicator and the principles stated in ISO
1996-2: 1987 (Amd 1:1998) and ISO 1996-1:2002.
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Measurement data in front of a façade or
another reflecting element must be corrected to exclude the reflected
contribution of this façade or element (as a general rule, this implies a 3
dB correction in case of measurement).
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THIRD SCHEDULE
MINIMUM REQUIREMENTS
FOR STRATEGIC NOISE MAPPING
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1. A strategic noise map is the
presentation of data on one of the following aspects:
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- an existing, a previous
or a predicted noise situation in terms of a noise indicator,
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- the exceeding of a
limit value,
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- the estimated number of
buildings, schools and hospitals in a certain area that are exposed to
specific values of a noise indicator,
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- the estimated number of
people located in an area exposed to noise.
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2. Strategic noise maps may be
presented to the public as:
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- graphical plots,
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- numerical data in
tables,
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- numerical data in
electronic form.
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3. Strategic noise maps for
agglomerations shall put a special emphasis on the noise emitted by:
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- road traffic,
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- rail traffic,
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- airports,
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- industrial activity
sites, including ports.
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4. Strategic noise mapping will be
used for the following purposes:
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- the provision of the
data to be sent to the Commission in accordance with article 5(4) and the
Fifth Schedule,
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- a source of information
for the general public in accordance with article 12,
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- a basis for action
plans in accordance with article 11(3).
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Each of those applications requires a
different type of strategic noise map.
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5. Minimum requirements for the
strategic noise maps concerning the data to be sent to the Commission are
set out in paragraphs 1.5, 1.6, 2.5, 2.6 and 2.7 of the Fifth Schedule.
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6. For the purposes of informing
the general public in accordance with article 12 and the development of
action plans in accordance with article 11(3), additional and more detailed
information must be given, such as:
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- a graphical
presentation,
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- maps disclosing the
exceeding of a limit value,
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- difference maps, in
which the existing situation is compared with various possible future
situations,
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- maps showing the value
of a noise indicator at a height other than 4 m where appropriate.
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The Agency may lay down rules on the types
and formats of these noise maps.
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7. Strategic noise maps for local
or national application must be made for an assessment height of 4 m and the
5 dB ranges of Lden and Lnight as required in the Fifth Schedule.
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8. For agglomerations separate
strategic noise maps must be made for road-traffic noise, rail-traffic
noise, aircraft noise and industrial noise. Maps for other sources may be
added.
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FOURTH
SCHEDULE
MINIMUM REQUIREMENTS FOR ACTION PLANS
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1. An action plan must at least
include the following elements:
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- a description of the
agglomeration, the major roads, the major railways or major airports and
other noise sources taken into account,
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- the authority
responsible,
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- the legal context,
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- any statutory limit
values in place,
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- a summary of the
results of the noise mapping,
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- an evaluation of the
estimated number of people exposed to noise, identification of problems and
situations that need to be improved,
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- a record of the public
consultations organised in accordance with article 11(6),
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- any noise-reduction
measures already in force and any projects in preparation,
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- actions which the
action planning authorities intend to take in the next five years, including
any measures to preserve quiet areas,
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- long-term strategy,
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- financial information
(if available): budgets, cost-effectiveness assessment, cost-benefit
assessment,
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- provisions envisaged
for evaluating the implementation and the results of the action plan.
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2. The actions which the action
planning authorities intend to take in the fields within their competence
may for example include:
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- traffic planning,
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- land-use planning,
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- technical measures at
noise sources,
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- selection of quieter
sources,
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- reduction of sound
transmission,
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- regulatory or economic
measures or incentives.
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3. Each action plan should contain
estimates in terms of the reduction of the number of people affected
(annoyed, sleep disturbed, or other).
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FIFTH
SCHEDULE
DATA TO BE SENT TO THE COMMISSION
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The data to be sent to the Commission are as
follows:
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1. For agglomerations
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1.1 A concise description of
the agglomeration: location, size, number of inhabitants.
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1.2 The responsible authority.
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1.3 Noise-control programmes
that have been carried out in the past and noise-control measures in place.
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1.4 The computation or
measurement methods that have been used.
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1.5 The estimated number of
people (in hundreds) living in buildings that are exposed to each of the
following bands of values of Lden in dB
4 m above the ground on the most exposed facade: 55-59, 60-64, 65-69, 70-74,
> 75, separately for noise from road, rail and air traffic, and from
industrial sources. The figures must be rounded to the nearest hundred (e.g.
5 200 = between 5 150 and 5 249; 100 = between 50 and 149; 0 = less than
50).
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In addition it should be stated, where appropriate and where such information
is available, how many persons in the above categories live in buildings
that have:
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- special insulation
against the noise in question, meaning special insulation of a building
against one or more types of environmental noise, combined with such
ventilation or air conditioning facilities that high values of insulation
against environmental noise can be maintained,
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- a quiet façade, meaning
the façade of a building at which the value of Lden
four metres above the ground and two metres in front of the façade, for the
noise emitted from a specific source, is more than 20 dB lower than at the
façade having the highest value of Lden.
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An indication should also be given on how major roads, major
railways and major airports as defined in Article 3 of the Directive
contribute to the above.
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1.6 The estimated total number
of people (in hundreds) living in buildings that are exposed to each of the
following bands of values of Lnight in
dB 4 m above the ground on the most exposed façade: 50-54, 55-59, 60-64,
65-69, > 70, separately for road, rail and air traffic and for industrial
sources. These data may also be assessed for value band 45-49 before the
date laid down in Article 11(1) of the Directive.
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In addition it should be stated, where appropriate and where such
information is available, how many persons in the above categories live in
buildings that have:
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- special insulation
against the noise in question, as defined in paragraph 1.5,
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- a quiet façade, as
defined in paragraph 1.5.
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It must also be indicated how major roads, major railways and major
airports contribute to the above.
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1.7 In case of graphical
presentation, strategic maps must at least show the 60, 65, 70 and 75 dB
contours.
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1.8 A summary of the action
plan covering all the important aspects referred to in the Fourth Schedule,
not exceeding ten pages in length.
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2. For major roads, major railways and major
airports
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2.1 A general description of
the roads, railways or airports: location, size, and data on the traffic.
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2.2 A characterisation of their
surroundings: agglomerations, villages, countryside or otherwise,
information on land use, other major noise sources.
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2.3 Noise-control programmes
that have been carried out in the past and noise-control measures in place.
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2.4 The computation or
measurement methods that have been used.
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2.5 The estimated total number
of people (in hundreds) living outside agglomerations in buildings that are
exposed to each of the following bands of values of Lden
in dB 4 m above the ground and on the most exposed façade: 55-59, 60-64,
65-69, 70-74, > 75.
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In addition it should be stated, where appropriate and where such
information is available, how many persons in the above categories live in
buildings that have:
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- special insulation
against the noise in question, as defined in paragraph 1.5,
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- a quiet façade, as
defined in paragraph 1.5.
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2.6 The estimated total number
of people (in hundreds) living outside agglomerations in buildings that are
exposed to each of the following bands of values of Lnight
in dB 4 m above the ground and on the most exposed façade: 50-54, 55-59,
60-64, 65-69, > 70. These data may also be assessed for value band 45-49
before the date laid down in Article 11(1) of the Directive.
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In addition it should be stated, where appropriate and where such
information is available, how many persons in the above categories live in
buildings that have:
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- special insulation
against the noise in question, as defined in paragraph 1.5,
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- a quiet façade, as
defined in paragraph 1.5.
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2.7 The total area (in km2)
exposed to values of Lden higher than
55, 65 and 75 dB respectively. The estimated total number of buildings (in
hundreds) and the estimated total number of people (in hundreds) living in
each of these areas must also be given. Those figures must include
agglomerations. The 55 and 65 dB contours must also be shown on one or more
maps that give information on the location of villages, towns and
agglomerations within those contours.
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2.8 A summary of the action
plan covering all the important aspects referred to in the Fourth Schedule,
not exceeding ten pages in length.
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Given under the Official Seal of the
Minister for the Environment, Heritage and Local Government this 29th
day of March 2006.
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DICK ROCHE
______________________
Minister for the Environment, Heritage and
Local Government.
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Explanatory Note
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(This note is not part of the instrument and does not purport to be a
legal interpretation)
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These Regulations transpose EU Directive 2002/49/EC relating to the assessment and
management of environmental noise. The Directive aims to provide a common
framework to avoid, prevent or reduce, on a prioritised basis, the harmful
effects of exposure to environmental noise.
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For the purposes of these Regulations,
environmental noise means unwanted or harmful outdoor sound created by human
activities, including noise emitted by means of transport, road traffic,
rail traffic, air traffic, and from sites of industrial activity including
those defined in Annex I to Council Directive 96/61/EC of 24 September 1996
concerning integrated pollution prevention and control. Types of noise not
included are noise that is caused by the exposed person, noise from domestic
activities, noise created by neighbours, noise at workplaces or noise inside
means of transport or due to military activities in military areas.
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The Regulations set out a two-stage process
for addressing environmental noise. Firstly, noise must be assessed through
the preparation of strategic noise maps for areas and infrastructure falling
within defined criteria, e.g. large agglomerations, major roads, railways
and airports. Secondly, based on the results of the mapping process, the
Regulations require the preparation of noise action plans for each area
concerned. The fundamental objective of action plans is the prevention and
reduction of environmental noise.
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The two-stage process will be implemented in
two phases; the first phase involving the areas identified in article 9(1)
of the Regulations and the second phase involving the areas identified in
article 9(2).
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The Regulations designate noise-mapping
bodies and action planning authorities for the making of strategic noise
maps and action plans. Primary responsibility for both noise mapping and
action planning is assigned to local authorities. While a number of other
bodies also have noise mapping functions, they will be carried out on behalf
of the local authorities concerned.
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The Regulations designate the Environmental
Protection Agency as the National Authority for the purposes of the
Regulations. The Agency's role includes supervisory, advisory and
coordination functions in relation to both noise mapping and action planning,
as well as reporting requirements for the purpose of the Directive.
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The Regulations provide for strategic noise
maps and action plans to be made available to the general public. They also
provide for public consultation on proposed action plans, and for the
results of public consultation to be taken into account in finalising action
plans or reviews of action plans.
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1 O.J. No. L189/12 of 18
July 2002.
2 O.J. No. L 257 of 10
October 1996, p. 26.
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