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DUBLIN DOCKLANDS AREA
Strategic EnvironmentalAssessment of theDraft Master Plan2003
DUBLIN DOCKLANDS DEVELOPMENT AUTHORITY
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DUBLIN DOCKLANDS AREA
Strategic EnvironmentalAssessment of theDraft Master Plan2003
Terry Prendergast, Dip.Env. Econs., BSc.(Surv.), M. Phil UDRP, MSc. SD, M.I.P.I., M.R.T.P.I.
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ii Dublin Docklands Area Strategic Environmental Assessment of the Draft Master Plan 2003
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CONTENTS
NON TECHNICAL SUMMARY iv
1 INTRODUCTION 11.1 EU Directive on SEA (Directive 2001/42/EC) 11.2 Dublin Docklands Area Master Plan Review 2003 1
2 METHODOLOGY 32.1 Scoping 32.2 Baseline Study 32.3 Consideration of Alternatives 32.4 Environmental Assessment of Master Plan Review 3
3 CONSISTENCY WITH NATIONAL/ REGIONAL/ 4LOCAL POLICY
3.1 Sustainable Development- A Strategy for 4Ireland, 1997
3.2 National Climate Change Strategy, 2000 43.3 Strategic Planning Guidelines for the 4
Greater Dublin Area, 19993.4 Residential Density Guidelines for Planning 4
Authorities, 19993.5 A Platform for Change, Strategy 2000 to 2016 43.6 Retail Planning Guidelines for Planning 5
Authorities, 20003.7 Dublin City Development Plan, 1999 5
4 CHARACTERISTICS OF THE EXISTING 7ENVIRONMENT IN THE DOCKLANDS AREA
4.1 Biodiversity/ Flora and Fauna 74.2 Population 84.3 Soil 94.4 Water 94.5 Air Quality 104.6 Climatic Factors 114.7 Noise 114.8 Material Assets/ Cultural Heritage 11
5 CONSIDERATION OF ALTERNATIVES 14
6 SUSTAINABILITY CRITERIA 15
7 ASSESSMENT OF MASTER PLAN REVIEW 167.1 Compatibility of Strategic Objectives 167.2 Compatibility of Strategic Objectives with 16
Sustainability Criteria7.3 Compatibility of Master Plan Review with 18
Sustainability Criteria
8 MITIGATION 26
9 MONITORING 27
10 OVERALL FINDINGS FROM THE ASSESSMENT 28
APPENDIX I 29APPENDIX II 30BIBLIOGRAPHY 31
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NON TECHNICAL SUMMARY
BACKGROUND
The EU Directive on Strategic Environmental Assessment or SEA
(Directive 2001/42/EC) came into force in July 2001 and requires
Member States to assess the likely significant environmental
effects of plans and programmes prior to their adoption, providing
for the assessment of strategic environmental considerations at an
early stage of the decision-making process. Each Member State
has until July 2004 to transpose the Directive into national law.
The Department of the Environment and Local Government
considers the Docklands Area to be an appropriate area to pilot
test SEA on a non-statutory basis in tandem with the review of
the 1997 Master Plan. It is anticipated that the experience
gained by the Authority in piloting SEA will provide an input to
proposed guidelines for planning authorities on SEA which the
Department intends drawing up as part of the process of the
general implementation of the Directive.
The EU Directive on SEA requires the carrying out of an
environmental assessment of plans and programmes which are
likely to have significant environmental effects and which set the
framework for future development consent of projects which
are subject to EIA or where an assessment is necessary due to
the likely effect on sites governed by the Habitats Directive
(Directive 92/43/EEC).
This document reports on the environmental assessment which
was carried out of the Master Plan Review. The report describes
the existing baseline environment in the Docklands Area and the
scoping exercise carried out. It also discusses the relationship
between the Master Plan Review with other plans and policies
and assesses the impact of its objectives and policies.
Both the Draft Master Plan Review and the accompanying SEA
Report are being made available to relevant authorities and to
the public.
DUBLIN DOCKLANDS AREA MASTER PLANREVIEW 2003
The Dublin Docklands Area Master Plan Review, prepared by the
Dublin Docklands Development Authority following public
consultation, outlines a strategy for “the sustainable social and
economic regeneration of the Area, with improvements to the
physical area being a vital ingredient”. The Review represents an
updating of the 1997 Master Plan and establishes the social and
economic framework for the redevelopment of the area,
identifying key strategic objectives and a range of policies.
Land use policies in the Review seek to achieve sustainable
development objectives with the Authority “pursuing a policy of
mixed-use development in the Docklands Area which would
achieve a sustainable environment integrating living, working
and leisure”. The aims of the Master Plan 1997 and the 2003
Review are ambitious; it is an overall objective that the
population of the Area increase by 25,000 and the number of
residential units increase by 8,000-11,000.
The Master Plan Review seeks to promote the development of an
integrated public transport system and imposes strict limitations
on car parking for new development. The provision of cycleways
and pedestrian routes is promoted.
The Review sets out design criteria for new development, seeking
to achieve high quality buildings and urban spaces. At the same
time, the Review seeks to conserve essential elements of the
built environment which contribute to the character of the area.
METHODOLOGY
The methodology devised to carry out the SEA of the Master
Plan Review reflected the requirements of the SEA Directive
while drawing on UK experience of environmental appraisal
of Development Plans.
The main steps taken in the process involved scoping, the
carrying out of a baseline study, the consideration of alternatives,
the environmental assessment of the objectives and policies of
the Master Plan Review and the formulation of mitigation and
monitoring measures.
1. Scoping
Scoping is a process which helps determine the direction and
focus of the SEA. Scoping for the SEA exercise in respect of the
Master Plan Review involved three stages. Firstly the Master Plan
Review was assessed for compatibility with relevant plans and
guidance documents at national, regional and local level, with
which it was found to be consistent.
Various organisations/government departments/statutory agencies
also were consulted in order to determine their opinion on the
issues which it is considered the SEA should cover. Details were
also sought on any information held by the relevant organisation
which would be relevant in the assessment of such issues. A list
of those consulted is included in Appendix I of this Report.
Responses were received from 9 of the 25 organisations/agencies/
departments contacted, with acknowledgements received from
a further two.
The third element of the scoping process involved drawing upon
the results of a public consultation exercise carried out as part of
the Master Plan Review by Mercator Marketing Research in
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association with Kelleher Associates. The outcome of the exercise
formed an important input into the drawing up of Sustainability
Criteria which formed the basis of the SEA assessment process.
2. Baseline Study
Baseline data was collected based on indicators described in the
SEA Directive ie biodiversity, population, human health, fauna,
flora, soil, water, air, climate factors, material assets, cultural
heritage including architectural and archaeological heritage and
landscape. It was found necessary to combine some indicators in
order to avoid unnecessary duplication. In addition human health
was not considered separately but arises under a variety of
indicators – population, water, air. As required by the SEA
Directive, the report also comments on the likely evolution of the
various indicators in the absence of the implementation of the
Master Plan Review.
Key findings of the baseline study are described below.
Biodiversity/Flora and Fauna
The Docklands Area possesses areas of diverse character
including existing built up areas, former industrial/port lands,
waterbodies, formally laid out open space areas and wildlife
areas. Much of the Docklands Area is not of significance in terms
of biodiversity of flora and fauna. Dúchas reports that there are
likely to be bats in the Area and that there may also be the
occasional visiting otter in the River Liffey and River Dodder.
Although the Royal and Grand Canals (including the Grand
Canal Basin) are included as proposed National Heritage Areas
(pNHA’s), the stretches of the canals located in the Docklands
Area, due to their proximity to built up areas and former industrial
railway and port lands, do not act as prominent wildlife channels.
In contrast, the adjoining South Dublin Bay is of significance in this
regard and is of international importance for nature conservation.
It is covered by three separate, but related, designations and is a
proposed National Heritage Area (pNHA), a candidate Special
Area of Conservation (SAC) and Special Protection Area (SPA).
Population
The Docklands Area has traditionally been made up of five
residential communities, centred loosely in villages within the
area. With the development of significant additional residential
units in IFSCI and II, the residential profile of the Area has been
strengthened considerably. The Docklands Area is continuing to
exhibit population increase. Over the period 1991-2000, the
population of the Area grew by c. 16%. The most vibrant area
of growth is evidenced in the 25-44 age cohort, with other age-
cohorts experiencing population decline. The increase in
population has been reflected in the increase in household units
in the Area, with the overall number of households increasing
from 6,042 in 1991 to 6,735 in 1996.
Reflecting the national economic growth of recent years and
increased participation in employment, a total of 42.2% of
Docklands residents were engaged in employment in 1996,
representing an increase of 5% since 1991. The ESRI estimates
that the labour force residing in the Docklands Area in 2000 was
in the order of 8,950 persons and that unemployment rates were
in the order of 10%.
The most important sector to the structure of employment in the
Area is commerce, which accounted for 20.4% of employment
among Docklands residents in 1996. The Professional Services
and Manufacturing sectors accounted for employment among
18.2% and 15.8% of Docklands residents respectively in 1996.
Community activity in Docklands is thriving with over 100
community groups and organisations in the Area.
Soil
Much of the Docklands Area is made up of reclaimed land. A
desktop study of former land uses within the Docklands Area,
together with site investigation data arising from development
proposals within the Area, indicates a variety of soil conditions
and that some sites have been contaminated by former
industrial uses or by the use of contaminated materials as part
of land reclamation.
Water
Waterbodies play an important role in defining the unique
character of the Docklands Area. Available data indicates that
the water quality of the waterbodies in the Area is generally
acceptable. The upgrading of the sewerage treatment plant at
Poolbeg, the Dublin Bay Project, will result in an improvement in
water quality in the River Liffey.
The Grand Canal Basin has been the most vulnerable of the water
bodies within the Area. Section 25 certification has issued to
Dublin City Council to extend an existing outfall through the
Grand Canal Basin and Authority’s lands to the north, to discharge
into the River Liffey, where its impact will not be significant.
Water Supply
To date, water supply in the Area has been catered for by the
existing pipe network. In order to cater for anticipated
development in the Area, particularly in the Docklands North
Lotts Area, the provision of new watermains to supply water
demand will be necessary.
Groundwater
A desktop study of former land uses within the Docklands Area
suggests that some contamination of the groundwater may have
occurred in the past. The extent of contamination will only
become evident on the carrying out of site-specific surveys.
Air Quality
Air quality levels for the Area for the most part fall within EU
guide levels. Nitrogen Oxide pollution however occurs at
individual hot spots or streets with very high traffic volumes.
Decreases in air pollution are anticipated arising from emission
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controls and stringent traffic management in Dublin City Centre
and the reduction in port traffic in the Area on the construction
of the Dublin Port Tunnel.
Noise
Environmental noise levels are high in those parts of the Area
located adjacent to heavily trafficked routes. A reduction in noise
values in the North Docklands Area is anticipated on the opening
of the Dublin Port Tunnel, with the expected decrease in HGV
traffic through the Area.
Material Assets/Cultural Heritage
The waterside location of the Docklands Area, in close proximity
to the city centre provides an area of unique character and
opportunity.
The Dublin City Development Plan, 1999, includes two Zones of
Archaeological Interest in the Area. Because the Area is made up
of land reclaimed from the inter-tidal estuary of the River Liffey
and the sea, any archaeological remains are likely to relate to
activities in the river estuary prior to reclamation. Industrial
archaeological features are dispersed throughout the Area as are
remnant features of the railway era.
The transport, maritime and industrial past of the Area has left a
legacy of buildings and other features, many of which are
Protected Structures, which contribute to the Area’s unique
character. Protected Structures are widely dispersed throughout
Docklands, some of which are of national/international
significance. A wide diversity exists in the range of Protected
Structures in the Area reflecting its maritime, transport and
docklands history. In addition, the Dublin City Development Plan,
1999, identifies six Conservation Areas in Docklands.
The waterbodies in Docklands play an important role in defining
the character of the Area in addition to providing a valuable
amenity and recreational resource. Whereas the River Liffey is the
great ‘form giver’ of the city, it also acts as a divide between
north and south river banks. The challenge exists to provide for
improved linkages while facilitating river regeneration. The other
key waterbodies in the Area are Grand Canal Dock, George’s
Dock, the Inner Dock, Spencer Dock and the River Dodder and
River Tolka. The former docks represent a unique architectural
and engineering achievement and act as a reminder of the
former port and industrial use of the Area.
The Docklands Area includes open space areas of diverse
character ranging from the formally set out Pearse Square to the
wilderness areas of Poolbeg. The Poolbeg Peninsula
accommodates amenity areas of city-wide significance. Indeed
few areas of the city exhibit the same variety of open spaces
which include parks, playgrounds, riverside, dockside and coastal
public amenity areas and walkways. Whereas the Area displays a
wide variety of open space areas, the the full potential of such
spaces may not be fully realised due to lack of public accessibility,
poor layout or public awareness.
Extensive views are available of the city from the Docklands Area
and of the Docklands Area from the city. The most significant
view corridor in this regard is the River Liffey. Views from Dublin
Bay and the south city are dominated by the Poolbeg Peninsula,
which forms a significant landmark feature but is unsightly when
viewed from the Beach Road area. Other views of Docklands are
available from a variety of vantage points and view corridors in
the city.
Non-implementation of Master Plan Review
Were the Master Plan Review not implemented, the
redevelopment of the Docklands Area would take place at a
slower pace than that envisaged in the 1997 Master Plan and
2003 Review. The traditional population of the Docklands Area
would naturally decline over time, with the profile of the
population (particularly in the traditional village communities)
gradually becoming older. The decline in population and older
age profile would have implications in terms of the provision of
infrastructure and services in the Area. Existing contaminated
sites would remain contaminated pending redevelopment. The
current situation regarding the waterbodies, water supply and
groundwater would remain largely unchanged. Current trends
regarding air quality and noise levels would be likely to continue.
The status quo would be likely to prevail in respect of Protected
Structures, Conservation Areas and sites/artefacts of archaeological
interest. The improvement of public access to the waterbodies,
the redevelopment of the Campshires, the provision of additional
amenity/open spaces including the redevelopment of areas
adjoining the waterbodies and river regeneration would stall.
3. Consideration of Alternatives
Two alternative options are available for consideration as part of
the SEA process:
• The ‘do nothing’ option.
• The option of not reviewing the 1997 Master Plan.
Under the ‘do nothing’ option, the Area would maintain its
current physical and socio-economic characteristics. Development
would be market dependant and would occur at a slower pace
and in a less co-ordinated manner. Investment by the Authority
would be absent. Adopting the ‘do nothing’ option would mean
that parts of the Area would remain derelict and under-utilised
with little physical, social or economic enhancement. This
alternative is not considered a viable option.
The second alternative is not to review the Master Plan 1997.
The Master Plan catered for the redevelopment/regeneration for
the Area for a 15 year timescale to 2012. Whereas the broad
thrust of the Master Plan is as valid today as in 1997,
background circumstances have in some instances changed. It is
considered necessary to reflect these changing circumstances,
which result in a shift in policy focus or emphasis. Thus the
alternative of not reviewing the 1997 Master Plan is likewise not
considered a viable option.
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4. Environmental Assessment of the Master Plan Review
The environmental assessment of the objectives and policies of
the Master Plan Review forms a major focus of this report. The
methodology used in the carrying out of the assessment employs
a series of matrices, the filling in of which led to a refinement
and refocusing of the objectives and policies of the Master Plan
Review. The objectives and policies were assessed against a set of
Sustainability Criteria. The Sustainability Criteria are listed in
Figure 1 of the main report and consist of a set of strategic
objectives, with a strong environmental/sustainable focus. The
Sustainability Criteria were devised taking into consideration the
findings of the community consultation process carried out to
date as part of the Master Plan Review and the scoping exercise
carried out as part of the SEA process.
In the filling out of the matrices, the impact, if any of the
Strategic Objectives or of selected policies of the Review, was
recorded. The matrices record the following; no link/effect,
beneficial effect/likely beneficial effect, deterioration of
environmental quality/conflict or uncertain effect, depending on
the nature of the matrix.
As part of the assessment the following were tested:
1. The internal compatibility of the Strategic Objectives of the
Master Plan Review were tested against each other, in order
to ensure that no tensions existed between the objectives
that could give rise to conflict. The assessment indicated no
conflicting objectives.
2. The Sustainability Criteria which had been devised were also
tested for compatibility to ensure that any tensions which
may exist between criteria were identified. No such conflicts
were identified.
3. The Strategic Objectives of the Master Plan Review were
tested against the Sustainability Criteria, with which they
were found to be largely compatible. The filling in of the
matrix indicated that:
a) additional noise will inevitable be a short term
consequence of the redevelopment of the Area;
b) new developments in the Area will impact in some small
way on greenhouse gas emissions. This is more than
counterbalanced by the fact that the area being
developed is a brownfield, former dockland area; and
c) the development of increased opportunities for local
employment in existing enterprises may result in a conflict
with some of the Sustainability Criteria. This is considered
inevitable.
4. Selected policies of the Master Plan Review were tested
against the Sustainability Criteria. Not every policy was tested.
Key policies were selected relevant to each section of the
Review for assessment. The filling in of the matrices
indicated that:
a) with a Plan of this nature, which covers a centrally
located, former dockland area with a wide variety of uses
and amenity areas, tensions are thrown up by some of
the proposed policies. In particular these tensions arise in
relation to policies which seek to consolidate/ expand
existing industrial or port use. There are valid socio-
economic reasons for the inclusion of such policies. Such
tensions cannot be avoided and are mitigated by the
requirement to avoid any adverse environmental impacts;
b) the need to incorporate sustainable design into modern
office developments, in order to reduce energy demand
and also contribute to meeting Ireland’s obligations to
greenhouse gas emissions under the Kyoto Protocol, is
also evident from the assessment. This is a wider issue,
with market forces playing a dominant role, but is one
which the Authority may bear in mind in assessing
proposals for development.
5. Mitigation Measures
The mitigation measures or key recommendations arising from
the SEA exercise comprise the inclusion in the Master Plan
Review of one additional Strategic Objective and two additional
policies and the refinement, combining, refocusing or simply the
shifting of policies from one section or another.
6. Monitoring
As part of the monitoring process, it is proposed to prepare an
annual monitoring report on the implementation of the Master
Plan. As indicated in the Master Plan Review, some indicators do
not lend themselves to annual monitoring. These would be more
appropriately dealt with on a five year basis. The Authority will
also co-operate with the relevant agencies in monitoring the
environmental impacts of the Master Plan. The Review also
incorporates two additional policies in respect of monitoring.
OVERALL FINDINGS FROM THE ASSESSMENT
It is clear from the assessment of the Strategic Objectives and
Policies of the Master Plan Review that the Review has a strong
sustainable thrust and focus. Almost all objectives and policies
were found to be either compatible or not in conflict with the
Sustainability Criteria devised for the assessment exercise. No
conflicting objectives or policies were evident. The mitigation
measures arising from the exercise can only be described as
minor in nature. The mitigation measures essentially remove
some duplication, clarify a number of policies and make good a
few policy omissions.
The exercise confirms that the Master Plan Review is a robust,
focussed and clearly thought out document that will continue to
provide a positive strategic framework for the development of
the Docklands Area.
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1 Dublin Docklands Area Strategic Environmental Assessment of the Draft Master Plan 2003
1 INTRODUCTION
The EU Directive on Strategic Environmental Assessment or SEA
(Directive 2001/42/EC) came into force in July 2001 and requires
Member States to assess the likely significant environmental
effects of plans and programmes prior to their adoption,
providing for the assessment of strategic environmental
considerations at an early stage of the decision-making process.
Each Member State has until July 2004 to transpose the Directive
into national law. The Department of the Environment and Local
Government considers the Docklands Area to be an appropriate
area to pilot test SEA on a non-statutory basis in tandem with
the review of the 1997 Master Plan. It is anticipated that the
experience gained by the Dublin Docklands Development
Authority – “the Authority” – in piloting SEA will provide an
input to proposed guidelines for planning authorities on SEA
which the Department intends drawing up as part of the process
of the general implementation of the Directive.
The assessment was carried out by Terry Prendergast, Dip. Env.
Econs., BSc (Surv), M. Phil UDRP, MSc SD, School of Real Estate
and Construction Economics, Dublin Institute of Technology, in
consultation with the Authority.
The report should be read in conjunction with the Master Plan
Review.
1.1 EU DIRECTIVE ON SEA (DIRECTIVE 2001/42/EC)
The EU Directive on SEA requires the carrying out of an
environmental assessment of plans and programmes which are
likely to have significant environmental effects and which set the
framework for future development consent of projects which are
subject to EIA or where an assessment is necessary due to the
likely effect on sites governed by the Habitats Directive (Directive
92/43/EEC).
Article 2 of the Directive defines environmental assessment as
“The preparation of an environmental report, the carrying out of
consultations, the taking into account of the environmental
report and the results of consultations in decision-making and
the provision of information on the decision……”.
The environmental report must identify, describe and evaluate
the likely significant effects on the environment of implementing
the plan and reasonable alternatives. Annex 1 of the Directive
details the information to be included in the environmental
report which can be summarised as follows:
• an outline of the contents and objectives of the
plan/programme and its relationship with other
plans/programmes;
• current environmental characteristics/conditions, including any
existing environmental problems, and the likely evolution
thereof without the implementation of the plan/programme;
• likely significant effects on the environment including on
issues such as biodiversity, population, human health, fauna,
flora, soil, water, air, climate factors, material assets, cultural
heritage including architectural and archaeological heritage,
landscape and the interrelationship between these factors;
• mitigation measures;
• reasons for selection of alternatives considered;
• description of monitoring measures; and
• non-technical summary.
In terms of consultation, the draft plan and environmental report
must be made available to relevant authorities and the public (as
identified by the Member State).
The environmental report and the outcome of the consultation
process must be taken into account during the preparation of
the plan, before its adoption. A statement is required which
summarises how environmental considerations have been
integrated into the plan and how the environmental report and
the results of the consultations carried out have been taken
into account.
The Directive obliges Member States to monitor the significant
environmental effects of the implementation of
plans/programmes. Existing monitoring arrangements may
be used, if appropriate.
1.2 DUBLIN DOCKLANDS AREA MASTER PLAN REVIEW 2003
The Dublin Docklands Area Master Plan Review, prepared by the
Authority following public consultation, outlines a strategy for
“the sustainable social and economic regeneration of the Area,
with improvements to the physical area being a vital ingredient”.
The Review represents an updating of the 1997 Master Plan for
the Area, which is generally recognised as a robust, integrated
and comprehensive document.
The Review seeks to integrate the social, economic and physical
development of the area, consistent with the objectives of the
Authority as set out in Section 18 of the Dublin Docklands
Development Authority Act, 1997. It is the duty of the Authority
to secure:
(i) the social and economic regeneration of the Dublin
Docklands Area, on a sustainable basis;
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(ii) improvements in the physical environment of the Dublin
Docklands Area; and
(iii) the continued development in the Custom House Docks Area
of services of, for and in support of, or ancillary to, the
financial sector of the economy.
The Review thus establishes the social and economic framework
for the redevelopment of the area, identifying key strategic
objectives and a range of policies.
Land use policies contained in the Review seek to achieve
sustainable development objectives with the Authority “pursuing
a policy of mixed-use development in the Docklands Area which
would achieve a sustainable environment integrating living,
working and leisure”. The aims of the Master Plan 1997 and the
2003 Review are ambitious; it is an overall objective that the
population of the Area increase by 25,000 and the number of
residential units increase by 8,000-11,000.
The Master Plan Review seeks to promote the development of an
integrated public transport system and imposes strict limitations
on car parking for new development. The provision of cycleways
and pedestrian routes is promoted.
The Review sets out design criteria for new development, seeking
to achieve high quality buildings and urban spaces. At the same
time, the Review seeks to conserve essential elements of the
built environment which contribute to the character of the Area.
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3 Dublin Docklands Area Strategic Environmental Assessment of the Draft Master Plan 2003
2 METHODOLOGY
The methodology devised to carry out the SEA of the Master
Plan Review reflected the requirements of the SEA Directive while
drawing on UK experience of environmental appraisal of
Development Plans. The recently published UK Draft Guidance
on SEA formed a useful input in the devising of the methodology
employed.
The main steps taken in the process are detailed below.
2.1 SCOPING
Scoping for the SEA process involved three stages.
(i) Relevant plans and guidance documents at national, regional
and local level were identified and their relationship with the
Master Plan Review identified and described. The Master Plan
Review was assessed for compatibility with the plans/guidance.
(ii) Various organisations/government departments/statutory
agencies were consulted in order to determine their opinion
on the issues which the SEA should cover. Details were also
sought on any information held by the relevant organisation
which would be of use in the assessment of such issues. A list
of those consulted is included in Appendix 1 of this Report.
Responses were received from 9 of the organisations/agencies/
departments contacted, with acknowledgements received from
a further two. Various issues were raised in the responses,
some of which were more relevant in terms of the Master
Plan Review rather than the SEA process. This reflects the
novelty of the SEA process and the lack of familiarity with
its characteristics.
(iii) As part of the Master Plan Review, Mercator Marketing
Research, in association with Kelleher Associates, were
engaged by the Authority to conduct a consultation exercise
with residents of the Docklands. The outcome of the research
conducted by Mercator Marketing Research/Kelleher
Associates formed an important input into the drawing up
of Sustainability Criteria which formed the basis of the SEA
assessment process (see Section 6.0).
2.2 BASELINE STUDY
Baseline data was collected, broadly based on indicators
described in the SEA Directive ie biodiversity, population, human
health, fauna, flora, soil, water, air, climate factors, material
assets, cultural heritage including architectural and
archaeological heritage and landscape. It was decided to conduct
the baseline study based on the indicators as detailed in the
Directive as the SEA exercise was being carried out at the request
of the DOELG in order to pilot test the Directive prior to its coming
into force. It was found necessary to combine some indicators in
order to avoid unnecessary duplication. In addition human health
came under a variety of indicators e.g. population, water, air.
No primary research was carried out in the collection of baseline
data. Existing data sources were used. The Environmental Impact
Statements carried out for the Grand Canal Dock Area and
Docklands North Lotts Area Planning Schemes formed important
data sources. The data on South Dublin Bay was largely extracted
from a consultant’s report prepared by Richard Webb, Natural
Environment Consultants Ltd., for the Authority in relation to the
Poolbeg Peninsula. EPA monitoring data was used in respect of
air quality in the Area. An ESRI report, The Employment and
Socio-Economic Profile of the Dublin Docklands Area, 2000,
provided, in the absence of up-to-date Census figures, the most
up-to-date data on the socio-economic characteristics of the
population of the Area.
The likely evolution of each of the indicators without the
implementation of the Master Plan Review was also described,
as required under the Directive.
2.3 CONSIDERATION OF ALTERNATIVES
Two alternative development options were available for
consideration as part of the SEA process:
• The ‘do nothing’ option.
• The option of not reviewing the Master Plan 1997.
These are dealt with in Section 5.0 of the report.
2.4 ENVIRONMENTAL ASSESSMENT OF THEMASTER PLAN REVIEW
The environmental assessment of the objectives and policies of
the Master Plan Review forms a major component of this report.
The methodology used in the carrying out of the assessment
employs a series of matrices, the filling in of which led to a
refinement and refocusing of the objectives and policies of the
Master Plan Review. As recommended in the UK Draft Guidance
on SEA, the objectives and policies were assessed against a set of
Sustainability Criteria. Although not required under the SEA
Directive, the formulation of Sustainability Criteria are “the key
way in which environmental and sustainability effects can be
identified, described, analysed, compared and monitored”
(ODPM, 2002, p.21). The Sustainability Criteria form a yardstick
against which the objectives and policies of the Master Plan
Review were tested. The criteria were devised taking into
consideration the findings of the community consultation process
carried out as part of the Master Plan Review and the scoping
exercise carried out as part of the SEA process.
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As part of the assessment the following were tested:
1. The internal compatibility of the Strategic Objectives of the
Master Plan Review were tested against each other, in order
to ensure that no tensions existed between the objectives
that could give rise to conflict.
2. The Sustainability Criteria which had been devised were also
tested for compatibility to ensure that any tensions which
may exist between criteria were identified. No such tensions
were identified and the exercise is included in Appendix II of
the report.
3. The Strategic Objectives of the Master Plan Review were
tested against the Sustainability Criteria.
4. Selected policies of the Master Plan Review were tested
against the Sustainability Criteria. In line with UK Draft
Guidance on SEA, not every policy was tested. Key policies
were selected relevant to each section of the Review
for assessment.
In the filling out of the matrices, the impact, if any, was recorded
indicating no link/effect, beneficial effect/likely beneficial effect,
some deterioration in environmental quality/conflict or uncertain
effect, depending on the nature of the matrix.
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5 Dublin Docklands Area Strategic Environmental Assessment of the Draft Master Plan 2003
3 CONSISTENCY WITH NATIONAL/REGIONAL/LOCAL POLICY
Since 1997 when the original Master Plan was adopted, a number
of strategic policy instruments have been introduced at national
and regional level with which the 2003 Master Plan Review is
required to be consistent with. These are detailed below. In
addition the Dublin City Development Plan was reviewed in 1999.
3.1 SUSTAINABLE DEVELOPMENT – A STRATEGY FOR IRELAND, 1997
The central aim of the Strategy is to apply principles of
sustainability systematically to policy-making and to integrate
them into the decision-making process.
The Strategy provides a comprehensive framework for the
promotion of sustainability across all strategic sectors. In terms of
urban regeneration, it seeks to bring redundant and derelict land
and buildings back into active use thus meeting key sustainable
objectives of reusing available resources, contributing to energy
efficiency, sustaining the urban fabric, reducing the need to develop
greenfield sites and protecting the countryside. The Master Plan
Review 2003 is consistent with the Strategy.
3.2 NATIONAL CLIMATE CHANGE STRATEGY, 2000
The National Climate Change Strategy provides a framework for
the achievement of reductions in greenhouse gas emissions as an
essential step in achieving the targets agreed under the Kyoto
Protocol. The Strategy is relevant to the Master Plan Review in
terms of both energy usage and transportation. The original
Master Plan and the Review aim to provide high quality buildings
and urban spaces in accordance with the principles of
sustainable development. The focus has been on the provision of
an efficient, flexible public transport system, in addition to
providing safe and attractive walking and cycling routes
throughout the entire Docklands Area. The Master Plan Review
2003 is consistent with the Strategy.
3.3 STRATEGIC PLANNING GUIDELINES FORTHE GREATER DUBLIN AREA, 1999
The Strategic Planning Guidelines for the Greater Dublin Area
were produced on behalf of the Dublin and Mid-East Regional
Authorities in 1997. A Review and Update was published in
2002. The Guidelines seek to put in place a strategic planning
framework for Development Plans and for future investment in
transport, sanitary services and other infrastructure in the overall
area. The Strategy distinguishes between the Metropolitan Area
and the Hinterland Area. The Strategy for the Metropolitan Area
is to follow a development path that will:
• consolidate development within the area;
• increase overall densities of development; and
• facilitate the provision of a considerably enhanced public
transport system and encourage a shift to public transport.
The Strategy seeks the maximum possible redevelopment of
brownfield sites and of infill development in the Metropolitan
Area. The Guidelines note that the greatest extent of brownfield
land occurs in the Docklands Area and state that the Strategy
should clearly incorporate the 1997 Master Plan objective to
accommodate an additional population of 25,000 in Docklands.
The Master Plan Review 2003 is consistent with the strategic
planning framework advanced in the Guidelines.
3.4 RESIDENTIAL DENSITY GUIDELINES FORPLANNING AUTHORITIES, 1999
The Residential Density Guidelines published by the Department
of the Environment and Local Government (DOELG) promote
increased residential densities in appropriate locations in town
and city centres, brownfield sites, inner suburban/infill and outer
suburban/greenfield sites, institutional lands and towns/villages.
The Guidelines note that in the case of significant brownfield sites,
proximate to existing or future transport corridors, the opportunity
exists for redevelopment to higher densities, subject to safeguards.
Firm emphasis is placed on the importance of qualitative standards
in achieving high quality design and layout; the objective should
be the achievement of an efficient use of land appropriate to its
context, while avoiding problems of over-development.
It is considered that the residential density standards adopted in
the Master Plan Review 2003 reflect and are consistent with the
Guidelines.
3.5 A PLATFORM FOR CHANGE, STRATEGY 2000 TO 2016
A Platform for Change, Strategy 2000 to 2016, published by the
DTO, promotes an integrated public transport network, strategic
but limited road network improvements, traffic and parking
policies, freight management policies, cycle and pedestrian
networks, demand management policy and guidance on
complementary land use policies.
The transportation policy of the Master Plan Review is consistent
with DTO policy.
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3.6 RETAIL PLANNING GUIDELINES FOR PLANNING AUTHORITIES, 2000 AND RETAIL PLANNING STRATEGY FOR THE GREATER DUBLIN AREA, 2001
The Retail Planning Guidelines for Planning Authorities, published
by the DOELG, provide a framework to guide the preparation of
Development Plans and to assess planning applications for retail
development. An objective of the framework is to support the
continuing role of town and district centres. The Guidelines
impose a convenience floorspace cap of 3,500 sq metres for
development within the Greater Dublin Area.
The Retail Planning Strategy for the Greater Dublin Area,
prepared for the local authorities in the GDA and the DOELG in
conjunction with the Dublin and Mid-East Regional Authorities,
was undertaken to ensure that Development Plans provide for
sufficient retail floorspace reflecting population and expenditure
growth, and that retail development is appropriately located.
The Strategy indicates Docklands as the location for the possible
development of a town/district centre.
The retail strategy proposed in the Master Plan Review is
consistent with current strategic retail policy.
3.7 DUBLIN CITY DEVELOPMENT PLAN, 1999
In accordance with Section 24 of the Dublin Docklands
Development Authority Act, 1997, Dublin City Council is required,
on the adoption by the Authority of a Master Plan, to consider
the need for consistency between the Dublin City Development
Plan and the Master Plan. The Dublin City Development Plan
1999 was adopted two years after the adoption of the Master
Plan 1997. While both plans broadly adopted a similar approach
to the planning and development of the Docklands Area, some
inconsistencies existed. The Master Plan Review updates and
reviews the 1997 Master Plan. As part of the review process,
consultations were held with Dublin City Council. In the
implementation of the Master Plan Review it will be important to
ensure that a consistent approach exists between both
authorities to the overall redevelopment of the Docklands Area.
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4 CHARACTERISTICS OF THEEXISTING ENVIRONMENT IN THE DOCKLANDS AREA
This section of the report describes the current state of the
environment in the Dublin Docklands Area – “the Area”, broadly
adopting the environmental indicators included in the SEA
Directive. Some indicators have been combined for the purpose
of clarity and to avoid duplication of information. Human health
was not considered separately but was considered to be either
directly or indirectly relevant to many of the indicators i.e. air,
water, material assets/cultural heritage, biodiversity.
The characteristics of the existing environment are described
under the following headings:
• Biodiversity/Flora and Fauna
• Population
• Soil
• Water
• Air
• Climate
• Material Assets/Cultural Heritage.
The Master Plan Review provides additional data describing the
existing environment.
As required by the SEA Directive, commentary is also included on
the likely evolution of the various indicators in the absence of the
implementation of the Master Plan Review.
4.1 BIODIVERSITY/FLORA AND FAUNA
The Docklands Area possesses areas of diverse character including
existing built up areas, former industrial/port lands, waterbodies,
formally laid out open space areas and wildlife areas. Much of
the Docklands Area is not of significance in terms of biodiversity
of flora and fauna. In contrast the adjoining South Dublin Bay is
of significance in this regard.
The Environmental Impact Statements prepared for the Grand
Canal Dock Area and Docklands North Lotts Area Planning
Schemes reported that flora on vacant and under-used sites in
both areas was dominated by species with the ability to tolerate
the unfavourable conditions that are found on such urban sites.
These include attributes such as:
• The ability to colonise the site by means of wind-borne seed;
• A life cycle that can contend with the stresses (particularly
drought) associated with the shallow soils that have
developed on concrete surfaces; and
• A life cycle and growth pattern that can tolerate varying
levels of trampling and disturbance.
At the time of the carrying out of the EISs no evidence existed in
either area of species registered for protection under the Wildlife
Act, 1976, the Flora Protection Order, 1999 or the annexes to
the Habitats Directive. Very little wildlife was evident in either
area. It was considered that pigeons and house sparrows were
present, but apart from the presence of brown rats and feral
cats, no evidence of mammals existed.
Although the Royal and Grand Canals (including the Grand
Canal Basin) are included as proposed National Heritage Areas
(pNHA’s), the stretches of the canals located in the Docklands
Area, due to their proximity to built up areas and former
industrial railway and port lands, do not act as prominent
wildlife channels.
Since the carrying out of the EIS’s however, Dúchas reports that
there are likely to be bats in the Area and that there may also be
the occasional visiting otter in the River Liffey and River Dodder.
South Dublin Bay
South Dublin Bay is of international importance for nature
conservation. The southern half of Dublin Bay is a large
triangular area stretching from the Poolbeg Peninsula to the
West Pier of Dun Laoghaire Harbour. It is a shallow estuarine
area which dries at low tide to expose over 800 hectares of sand,
bisected by several deep channels. Beneath the surface of the
sand there are huge numbers of a few key invertebrates such as
the cockle, ragworm and a tiny marine snail called hydrobia
which can occur at densities of greater than 16,000 per square
metre. These invertebrates provide food resources for large flocks
of birds, especially in winter when they migrate south from arctic
breeding grounds. The birds move freely between different parts
of Dublin Bay with many feeding on Sandymount and Merrion
Strands at low tide and roosting at the North Bull Island at high
tide. There are also a number of smaller high tide roosts around
South Dublin Bay, including the shoreline near Poolbeg
Generating Station.
The average peak winter population in the whole of Dublin Bay
was over 31,000 in the period from 1994 to 1998. Four species
– brent goose, knot, bar-tailed godwit and redshank – occur in
internationally important numbers with a further 14 species
present in nationally important numbers. Among the most
obvious of the waders are oystercatchers with their black and
white plumage and bright red bills. The most significant wildfowl
are the brent geese which often form large flocks on coastal
grassland. There are also large numbers of gulls, especially the
black-headed gull, attracted by the wastewater treatment works
at Poolbeg. In late summer the shoreline of South Dublin Bay is
used by large flocks of terns for night-time roostings.
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A number of studies of the birds of Dublin Bay have been carried
out including ongoing monitoring for the Dublin Bay Project by
Dublin City Council. Findings show that the strand between
Merrion Gates and Seapoint is the preferred area for the majority
of birds, but, at certain stages of the tide, large numbers also
occur in the northern sectors, close to the Poolbeg Peninsula. In
late winter, brent geese switch from feeding in the intertidal area
to grazing on costal grassland. A number of sites are used on the
peninsula including Sean Moore Park and Ringsend Park.
South Dublin Bay is covered by three separate, but related,
designations:
Proposed National Heritage Area. The primary importance of the
pNHA is as an internationally important site for waterbirds. The
boundary of the pNHA follows the high water mark. In addition,
there is a very small pNHA which covers two mooring dolphins in
the River Liffey near Pigeon House Harbour as these are used by
nesting terns.
Candidate Special Area of Conservation (SAC). This statutory
designation recognises the importance of the bay as a prime
wildlife conservation area of European significance. The
boundary of the SAC coincides with that of the pNHA.
Special Protection Area (SPA). This statutory designation
recognises the importance of the bay to birds and requires the
prevention of pollution, or deterioration of habitats or any
disturbance to birds which use the SPA.
Non-implementation of Master Plan Review
Were the Master Plan Review not implemented, the
redevelopment of the Docklands Area would take place at a
slower pace than that envisaged in the Master Plan 1997 and
Review. Any proposed development adjacent to the South Dublin
Bay Area would be required to reflect its significance in terms of
nature designation.
4.2 POPULATION
The Docklands Area has traditionally been made up of five
residential communities, centred loosely in villages within the
area, three on the north side and two on the south side. These
are East Wall, North Strand, Sheriff Street/North Wall, City Quay/
Westland Row and Ringsend/Irishtown. With the development of
significant additional residential units in IFSCI and II, the residential
profile of the Area has been strengthened considerably.
The socio-economic profile of the Area is outlined in Chapter 2
of the Master Plan Review. Key indicators are as follows:
• The Docklands Area is continuing to exhibit population
increase, with the overall population increasing from 16,713
persons in 1991 to 17,425 in 1996 and 19,467 persons in
2002. Over the period 1991-2002, the population of the
Area grew by c. 16%.
• The most vibrant area of growth is evidenced in the 25-44
age cohort, with other age-cohorts experiencing population
decline. This has had consequences in terms of the provision
of services in the Area. For example, the decline in the 0-14
age cohort has resulted in declining school numbers
throughout the Area. It is also reflected in the characteristics
of household units in the Area.
• The increase in population has been reflected in the increase
in household units in the Area, with the overall number of
households increasing from 6,042 in 1991 to 6,735 in 1996
representing an absolute growth of 693 households over the
period or 11.5%. Data on the number of household units
currently in existence in the Area will become available on the
full publication of the results of the 2002 Census.
• Reflecting the population profile of the Area, the number of
one-person households is greater than in Dublin City and
County.
• Reflecting the national economic growth of recent years and
increased participation in employment, a total of 42.2% of
Docklands residents were engaged in employment in 1996.
Although still below the comparable percentage for the GDA
of 49.6%, it represented an increase of 5% since 1991. It is
anticipated that labour force participation rates will show
further increases when the full results of the 2002 Census
become available. The ESRI estimates that the labour force
residing in the Docklands Area in 2000 was in the order of
8,950 persons and that unemployment rates were in the
order of 10%, with the number of unemployed estimated to
have fallen substantially since 1996.
• Reflecting the proximity of the Area to the city centre and the
growth of office development in the Docklands Area, the most
important sector to the structure of employment in the Area
is commerce, which accounted for 20.4% of employment
among Docklands residents in 1996, representing a 4.3%
increase since 1991. The importance of the sector is expected
to have strengthened since that time. The Professional Services
and Manufacturing sectors accounted for employment
among 18.2% and 15.8% of Docklands residents respectively
in 1996. The latter had fallen by 4.6% from 1991, illustrating
the replacement of manufacturing with office use in the Area.
• Community activity in Docklands is thriving with over 100
community groups and organisations in the Area. The groups/
organisations cater for a wide range of activities and interests
including educational assistance, community development
and training, crèches and playgroups, parish work, sports and
youth activity, support for the elderly, enterprise /
employment advice and training etc.
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Non-implementation of Master Plan Review
Were the Master Plan Review not implemented, the
redevelopment and renewal of the Area would take place at a
much reduced pace. The rate of growth of the residential
population would not take place at the rate anticipated in the
Master Plan. Meanwhile the traditional population of the
Docklands Area would naturally decline over time, with the
profile of the population gradually becoming older. The decline
in population and older age profile would have implications in
terms of the provision of infrastructure and services in the Area.
4.3 SOIL
Much of the Docklands Area is made up of reclaimed land.
The geology underneath the layers of fill comprise alluvial
deposits including interbedded silts, sands and gravels underlain
with glacially deposited boulder clay with sands and gravels over
a limestone bedrock. Information obtained from previous site
investigations in the general area of the proposed development
indicates the following typical geo-technical characteristics of the
various layers. See Table 1
A desktop study of former land uses within the Docklands Area,
together with site investigation data from development proposals
within the Area, indicates a variety of soil conditions and that
some sites have been contaminated by former industrial uses or
by the use of contaminated materials as part of land reclamation.
This is consistent with Dockland areas internationally, reflecting
the nature and character of such areas. One heavily
contaminated site, the former gasworks site on Sir John
Rogerson’s Quay, representing an area of 24 acres, has been
recently decontaminated by the Authority.
To date no national survey has been carried out to identify and
register contaminated sites. The detailed extent of contamination
in the Area is beyond the scope of this report and will need to
be determined by site-specific surveys.
Non-implementation of Master Plan Review
Were the policies and objectives of the Master Plan Review not
to be implemented, the likelihood is that, in the absence of
redevelopment of the Area, existing contaminated sites would
remain contaminated pending redevelopment.
4.4 WATER
Waterbodies play an important role in defining the unique
character of the Docklands Area. The water quality of those
waterbodies for which data is available is as follows:
River Liffey
Water quality in the river is that of a typical lowland, urban river.
Previous studies have revealed that the river has moderate
pollution levels. The quality of the water deteriorates as the river
becomes tidal. The part of the river near the Docklands Area is
affected by the tide and there is a discernible increase of salinity
and pollutants such as suspended solids, ammonia and heavy
metals at this location. This is due to the sediments being
disturbed and the plug effects of the tide, which have pushed
materials from the sewage outfall at Poolbeg back up the river.
The upgrading of the treatment plant, to include forms of
secondary and tertiary treatment, will result in an improvement
in water quality in the river.
River Dodder
The water quality of the Lower Dodder is similar to that of the
Liffey. It is high in ammonia and heavy metals. The biological
oxygen demand (BOD) is however acceptable. The river is
polluted at the Grand Canal Dock end despite the tidal
influences.
Grand Canal Basin/Grand Canal
The Grand Canal Basin has been the most vulnerable of the
water bodies within the Area. The long retention time and low
throughput of water makes it similar to a small lake and is
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Layer Description Layer Characteristics Probable Depths of Layer
Filled Ground Gravelly clay filled with fragements of From existing ground to 5 metresglass, clay, brick, plastics, metal, timber, ash and ceramics
Soft Black Silty Clay Alluvial deposits ranging from 1 to 2 1 to 2 metresmetres thick and generall soft flow sheer strength
Glacial Boulder Clay Stiff to hard with occassional inerbedded 3 to 10 metresgravel layers
Limestone Varies from weak to moderately strong 7 to 20 metresand strong to very strong
Table 1
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particularly susceptible to pollution through leaching or direct
discharge of both solid and liquid material from the sites around it.
The Grand Canal is a freshwater waterbody and not affected by
the tide. It is free from heavy metals and as it passes through
the centre of the Basin the canal has a good biological status
with a low BOD and chemical oxygen demand (COD). As it
enters the Basin the suspended solids concentration falls as
expected due to enhanced settlement and flocculation in the
large enclosed area. A significant increase in BOD formerly
existed in the Basin adjacent to the contaminated former Dublin
Gas production site. This site has since been decontaminated by
the Authority.
Water quality within the Grand Canal Basin has been adversely
affected in recent years by an outfall, which, although primarily
consisting of surface water, can contain some foul sewage and
discharges directly into the southern end of the inner basin
during periods of heavy rainfall. Section 25 certification has
issued to Dublin City Council to extend the outfall through the
Grand Canal Basin and Authority’s lands to the north, to discharge
into the River Liffey, where its impact will not be significant.
George’s Dock/Inner Dock
The water quality in both George’s Dock and the Inner Dock has
improved through the actions of the Authority. Aeration has
been introduced into both docks and water quality is satisfactory.
Spencer Dock/Royal Canal
The long retention time and low throughput of water makes this
waterbody somewhat similar to a small lake and hence it is
susceptible to pollution through leachate or discharges from
adjoining lands.
Water Supply
To date, water supply in the Area has been catered for by the
existing pipe network. This has proved adequate to meet
demands, although water pressure has been relatively low. In
order to cater for anticipated development in the Area, in
particular in the Docklands North Lotts Area, the provision of
new watermains to supply water demand will be necessary.
Groundwater
A desktop study of former land uses within the Docklands Area
suggests that some contamination of the groundwater may have
occurred in the past. The extent of contamination will only
become evident on the carrying out of site-specific surveys. No
data exists at national level of groundwater conditions in the Area.
Non-implementation of Master Plan Review
In the event of non-implementation of the Master Plan Review,
the situation regarding the waterbodies, water supply and
groundwater would remain unchanged. In particular, river
regeneration would be stalled.
4.5 AIR QUALITY
Data on the levels of the main air pollutants monitored in Ireland
in 2000 are available from the Environmental Protection Agency
(EPA, 2000). As noted by the Agency, air quality monitoring in
Ireland remains concentrated mainly on smoke and sulphur
dioxide (SO2), with less comprehensive data available for other
pollutants.
Smoke and Sulphur Dioxide (SO2),
Dublin City Council maintains one fixed monitoring station for
these two pollutants in the Docklands Area, which is located at
Ringsend. The air quality standards currently in force for smoke
and SO2 are based on EC Directive 80/779/EEC. The annual
mean guide values for smoke and SO2 are 40 to 60 ug/m3
respectively. Maximum daily mean values are 100 to 150 ug/m3.
(i) Smoke
The annual mean level recorded at Ringsend in the 2000/2001
monitoring period was 7ug/m3, well below guide levels. The
ban on the sale of bituminous coal in Dublin since October
1990 has resulted in a dramatic reduction in smoke levels.
(ii) Sulphur Dioxide (SO2)
The mean SO2 concentration values recorded in Dublin City
for 2000/2001 were very low, with an annual mean value of
6 ug/m3 recorded at Ringsend. The EPA notes that this reflects
the occurrence of alkaline levels in the titration process
(EPA, 2000).
Particulate Matter
Concentration of PM10 are monitored at four sites in Dublin
City; College Street, Coleraine Street, Rathmines and the Phoenix
Park. Recorded levels of PM10 have exceeded recommended
levels at College Street, which the EPA notes are clearly due to
traffic impacts. The Agency also notes that the location of the
kerbside monitoring site is not in compliance with the EU Directive.
In addition, in 2000 the EPA deployed mobile monitoring units to
record levels of PM10 in selected locations. One such location was
Pearse Street, Dublin 2. The Agency stresses that the temporal
coverage of the selected sites is insufficient to allow for a full
assessment. The average PM10 value recorded for the site was
33 ug/m3 which was within the relevant Directive (Directive
1999/30/EC) limit value.
Nitrogen Oxides (NOx and NO2)
The EPA reports data for nitrogen oxides for five fixed sites, in
addition to results from five mobile units. One of the mobile
units is again located at Pearse Street, Dublin 2. In general, levels
of NO2 measured at the monitoring stations did not exceed limit
values set in the relevant EC Directives (Directives 85/203/EEC
and 1999/30/EC). The EPA however notes that the levels
measured at Pearse Street were significantly higher than those
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measured at other sites, reflecting the high levels of traffic and
traffic congestion occurring on the street. The EPA concludes
that NO2 pollution is likely to be confined to hot-spot areas or
individual streets with very high traffic volumes.
Lead
Emissions from petrol motor vehicles are the main source of lead
in the atmosphere. With the introduction of unleaded petrol,
concentrations of this pollutant have decreased significantly.
Levels recorded at monitoring sites in Dublin City (including
Pearse Street) are well below EU limit values.
Carbon Monoxide/Benzene
Engine exhausts and space heating flues using certain fuels
provide the main source of carbon monoxide (CO), while benzene
is a constituent of crude oil and exists in petrol. Data on carbon
monoxide and benzene levels for Dublin is available for one fixed
monitoring site located at Wood Quay and indicates that levels
comply with the EU limit values. Data recorded by the EPA mobile
unit at Pearse Street recorded levels well below EU limit values.
Non-implementation of Master Plan Review
At present, air pollution occurs in the vicinity of heavily trafficked
routes, arising from emissions from vehicles. Decreases in air
pollution are anticipated arising from emission controls and
stringent traffic management in Dublin City Centre and the
reduction in port traffic in the Area on the construction of the
Dublin Port Tunnel. In the absence of the implementation of the
Master Plan Review, current trends in this regard would continue.
4.6 CLIMATIC FACTORS
Ireland ratified the UN Framework Convention on Climate
Change in 1994 and the Kyoto Protocol in 1997. Under the
latter, Ireland has agreed to limit the net growth of greenhouse
gases to 13% above the 1990 level by the period 2008-2012.
Achievement of this growth level is giving rise to and will
continue to pose a real challenge.
Dublin’s climate is classified as temperate with monthly
temperatures ranging from 5-15ºC. Rainfall within the city is
50mm per annum (with wetter weather between November-
January). South-westerly winds predominate. The annual
precipitation (30 year average) recorded in Merrion Square is
710mm. Records show that there have been 21 periods of
absolute drought (15 or more consecutive days with <0.2mm of
precipitation) over a 25 year period (1960-1984).
The climate and micro-climate of the Area is characteristic of a
site adjacent to a river. The effect of the coastal breeze (on-shore
during the day, off-shore at night time) is particularly significant
at the mouth of the River Liffey, resulting in a low level easterly
wind during the day, especially during the summer months. In
addition, light on-shore winds along the Liffey Valley may also
develop during the daytime on relatively calm winter days. This
can significantly effect the dispersion of low level air pollution
emissions in Dublin and result in a more rapid break up of fog
conditions than would occur further inland.
Micro climatic changes will occur arising from the development
of the Docklands Area. These changes will be particularly evident
in the Grand Canal Dock and Docklands North Lotts Areas,
which at present lack shelter and are windswept. Such local
climatic changes will be relatively minor in nature.
Non-implementation of Master Plan Review
In the event of either the implementation or the
non-implementation of the Master Plan Review, climatic conditions
in the Docklands Area will remain largely unchanged. Micro
climatic changes will occur at a slower pace in the event of
non-implementation.
4.7 NOISE
No independent data on noise levels in the Docklands Area is
available at national or local level. From the Authority’s
observations and from noise surveys carried out as part of
development proposals in the Area, it is clear that environmental
noise levels are high in those parts of the Area located adjacent
to heavily trafficked routes.
Non-implementation of Master Plan Review
In the absence of the implementation of the Master Plan Review
current trends are likely to continue in this regard. Some
reduction in noise levels in the North Docklands Area is likely to
arise on the opening of the Dublin Port Tunnel, with the
anticipated resultant decrease in HGV traffic through the Area.
4.8 MATERIAL ASSETS/CULTURAL HERITAGE
The waterside location of the Docklands Area, in close proximity
to the city centre provides an area of unique character and
opportunity. The Area is not homogenous in nature and is
characterised by a mix of high quality redeveloped areas,
traditional village communities, major utility and amenity uses,
industrial land, wildlife areas and underutilised/derelict sites. The
material assets/cultural heritage of the Area are outlined under
the categories detailed below:
(i) Archaeology
(ii) Protected Structures/Conservation Areas
(iii) Waterbodies
(iv) Open spaces
(v) Views
(i) Archaeology
Because the Area is made up of land reclaimed from the
inter-tidal estuary of the River Liffey and the sea, any
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archaeological remains are likely to relate to activities in the
river estuary prior to reclamation. The Dublin City
Development Plan, 1999, includes two Zones of
Archaeological Interest in the Area; one centred on
Thorncastle Street, Ringsend and the other centred around
the junction of Irishtown Road and Bath Street, Irishtown.
Recent archaeological investigations of a site located at
Thorncastle Street in the Zone of Archaeological Interest
yielded no archaeological remains.
Visible remains relate to industrial archaeology, remnants of
which are dispersed throughout the Area. These include the
former docks, campshires, mooring rings, bollards, steps,
machinery etc. Other remnant features of the railway era are
also evidenced in the Area and include rails, viaduct,
footbridges etc.
Parts of the Docklands Area are included as recorded
archaeological monuments under Section 12 of the National
Monument (Amendment) Act, 1994. These include:
• Custom House Quay/North Wall Quay
• City Quay/Sir John Rogerson’s Quay
• The sea wall at York Road/Pigeon House Road/South Wall
(ii) Protected Structures/Conservation Areas
As noted in the Master Plan Review, the transport, maritime
and industrial past of the Area has left a legacy of buildings
and other features, many of which are Protected Structures,
which contribute to the Area’s unique character.
Protected Structures are widely dispersed throughout the
Area, some of which are of national/international significance.
These include Gandon’s eighteenth century masterpiece, the
Custom House; one of the most extensive and finest early
nineteenth century cast-iron roof systems in Europe at Stack
A and the outstanding achievement of the South Wall. In
general however the number of Protected Structures in the
Area is relatively low, reflecting the fact that the Area
comprises reclaimed land, a large proportion of which was
subsequently used for port and industrial use. This is
evidenced in the Docklands North Lotts Area, one of the main
redevelopment areas in Docklands, which contains relatively
few Protected Structures. A wide diversity however exists in
the range of Protected Structures in the Area reflecting its
maritime, transport and docklands history. Protected
Structures include former gasometer support structures,
railway viaducts, a former power station, docks, bridges and
warehouses.
The Dublin City Development Plan, 1999, identifies a number
of Conservation Areas in Docklands at the following
locations:
• The River Liffey including quaysides
• Grand Canal Dock/Grand Canal
• George’s Dock
• Spencer Dock/Royal Canal
• The Custom House
• The River Dodder
Whereas the number of Protected Structures in the Area may
be relatively low, the high proportion of the Area covered by
Conservation Area status reflects the unique character and
environmental quality of parts of the Area.
Non-implementation of Master Plan Review
In the event that the Master Plan is not implemented, the
status quo is likely to prevail. Redevelopment and renewal
would be likely to occur in a piecemeal fashion, rather than in
the comprehensive manner envisaged. Against this
background, the opportunities for introducing new uses for
Protected Structures would be more limited. The character of
the existing Conservation Areas would remain largely
unaltered in the shorter term. Sites/artefacts of archaeological
interest would be largely unaffected.
(iii) Waterbodies
The waterbodies in Docklands play an important role in
defining the character of the Area in addition to providing a
valuable amenity and recreational resource. As noted in the
Master Plan, the River Liffey is the great ‘form giver’ of the
city and the Docklands Area. The containment of the river to
create a channel for shipping resulted in land reclamation on
either bank, giving the Docklands Area the form it has today,
deriving from the simple orthogonal grid pattern of streets
and development blocks which were laid out in the early
eighteenth century. Reflecting the critical role of the river, the
Liffey Quays from Spencer Dock eastwards are designated as a
Conservation Area in the Dublin City Development Plan, 1999.
In terms of recreational use, the river is used for cruise
ship/visiting ship or boat berthage, canoeing and boat racing.
The Liffey Swim and Liffey Descent are annual events. Secure
visitor moorings are available at the Authority’s offices. The
redevelopment of the campshires for public amenity use is
ongoing. Whereas the Liffey is the great ‘form giver’ of the
city, it also acts as a divide between north and south river
banks. East of Matt Talbot Bridge linkage across the river is
particularly weak. The development of the Macken Street and
Lombard Street Bridges will address this and improve
accessibility significantly. The challenge exists to provide for
improved linkages while facilitating river regeneration.
The other key waterbodies in the Area are Grand Canal Dock,
George’s Dock, the Inner Dock, Spencer Dock and the River
Dodder and River Tolka. The former docks represent a unique
architectural and engineering achievement and act as a
reminder of the former port and industrial use of the Area.
Public access is available to George’s Dock, the Inner Dock
and parts of Grand Canal Dock. The public will have access
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to Spencer Dock on redevelopment of the adjoining lands to
the east. Another waterbody in the Area at Poolbeg Harbour
is in the ownership of the ESB. Public access is not available
to the harbour.
Watersports activities take place on Grand Canal Dock. The
recently constructed pontoon at George’s Dock allows for the
mooring of barges for restaurant/retail use alongside. The
Inner Dock acts as a key amenity space in the Area.
Reflecting the contribution played by the waterbodies in
defining the character of the Docklands Area, Grand Canal
Dock, George’s Dock, Spencer Dock and those sections of the
River Dodder and River Tolka located within the Docklands
Area are included as Conservation Areas in the Dublin City
Development Plan, 1999. Poolbeg Harbour is also included as
a Conservation Area in the Plan. In conjunction with their
Conservation Area status, George’s Dock, the Inner Dock and
Grand Canal Dock are designated as Protected Structures.
Non-implementation of Master Plan Review
In the absence of the implementation of the Master Plan
Review, the status quo would remain. The improvement of
public access to the waterbodies, the redevelopment of the
Campshires, the redevelopment of areas adjoining the
waterbodies and river regeneration would stall.
(iv) Open Spaces
The Docklands Area includes open space areas of diverse
character ranging from the formally set out Pearse Square to
the wilderness areas of Poolbeg. Indeed few areas of the city
exhibit the same variety of open spaces which include parks,
playgrounds, riverside/dockside walkways and coastal public
amenity areas.
Whereas the Area displays a wide variety of open space areas,
the Master Plan Review acknowledges that the full potential
of such spaces is frequently not fully realised due to lack of
public accessibility, poor layout or public awareness.
Open space provision is generous in the South Docklands
Area and will be augmented by further development of the
Campshires along their full extent and the development of
amenity areas alongside Grand Canal Dock, in addition to the
development of Grand Canal Square and smaller urban
squares. A total of over 30 hectares of open space is available
in Ringsend Park, Sean Moore Park, Irishtown Park and
smaller spaces such as Pearse Square.
The North Docklands Area is less well provided for in terms of
parkland. Fairview Park adjoins the Area and is in easy proximity
of the East Wall and North Strand communities. Development
of the Campshires is ongoing along North Wall Quay.
The Poolbeg Peninsula accommodates amenity areas of city-
wide significance. These comprise the coastal walkway, the
Irishtown Nature Park and the South Wall. The latter is
designated both as a Conservation Area and a Protected
Structure in the Dublin City Development Plan, 1999.
Non-implementation of Master Plan Review
In the event of non-implementation of the Master Plan
Review, the status quo would prevail, with the provision of
additional amenity/open spaces in the Area stalled.
(v) Views
Extensive views are available of the city from the Docklands
Area and of the Docklands Area from the city. The most
significant view corridor in this regard is the River Liffey.
Views eastwards from Dublin City of the river are however
disrupted by the prevalence of vacant and underutilised sites,
the lack of a coherent urban form and the presence of former
warehouse buildings on the Campshires.
Views from Dublin Bay and the south city are dominated by
the Poolbeg Peninsula, which forms a significant landmark
feature with its low rise land mass punctuated by high power
generating chimneys, piled containers and a variety of utility
and industrial buildings.
Other views of Docklands are available from a variety of
vantage points and view corridors in the city. Of particularly
significance is the Fitzwilliam Street View Corridor which runs
in a northerly direction from Fitzwilliam Street and which
impacts on development in the western section of the
Docklands North Lotts Area.
Non-implementation of Master Plan Review
In the event that the Master Plan Review were not
implemented, views of the Area would undergo change at
a slower pace than would arise on implementation of
the Review.
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5 CONSIDERATION OF ALTERNATIVES
As noted in Section 2.3, two alternative options were considered
to be available for assessment as part of the SEA process:
• The ‘do-nothing’ option
• The option of not reviewing the existing Master Plan 1997.
Under the ‘do nothing’ option, the Area would maintain its
current physical and socio-economic characteristics. Development
would be market dependant and would occur at a slower pace
and in a less co-ordinated manner. Investment by the Authority
would be absent. Adopting the ‘do-nothing’ option would mean
that parts of the Area would remain derelict and under-utilised
with little physical, social or economic enhancement. In this
context the establishment by Government of the Authority under
the Dublin Docklands Development Authority Act, 1997, with
the remit of the social, economic and physical enhancement of
the Area, presupposes that the Area is in need of regeneration,
and that the ‘do-nothing’ alternative is not a viable option.
The second alternative is not to review the Master Plan 1997.
The Master Plan catered for the redevelopment/regeneration for
the Area for a 15 year timescale to 2012. The Master Plan has a
wide level of acceptance and recognition, and not conducting a
review of the Plan would be a viable alternative. However,
whereas the broad thrust of the Master Plan is as valid today as
in 1997, background circumstances have in some instances
changed. It is considered necessary to reflect these changing
circumstances, which can result in a shift in policy focus or
emphasis. Thus the alternative of not reviewing the Master Plan
1997 is likewise not considered an appropriate option.
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6 SUSTAINABILITY CRITERIAAs noted earlier, the Master Plan Review outlines a strategy for
“the sustainable social and economic regeneration of the Area,
with improvements to the physical environment being a vital
ingredient.” This section of the report sets out a set of
Sustainability Criteria which form the basis for an appraisal of
the objectives and policies contained in the Review. The criteria
are listed in Figure 1 overleaf. The findings of the community
consultation process, carried out as part of the Master Plan
Review, formed an important input in the drawing up of the
Sustainability Criteria. The Sustainability Criteria are broadly
categorised in terms of the indicators outlined in the SEA
Directive. Again, some indicators are combined to avoid
repetition. Human health is not dealt with under a separate
category but arises under a variety of categories below e.g.
population, air and water. In the course of the carrying out of the
appraisal, the Sustainability Criteria were refined, combined and
clarified in order to avoid duplication and ensure a clear, focused
set of criteria against which to measure the Master Plan Review.
The Sustainability Criteria were also checked against the objectives
formulated in “Sustainable Development – a Strategy for Ireland”
(DOE, 1997), with which they were found to be consistent.
FIGURE 1 - SUSTAINABILITY CRITERIA
Bio diversity/Flora and Fauna
B1 - safeguard designated areas/ areas of nature
conservation importance while increasing potential for
wildlife/flora and fauna, where appropriate.
Population
P1 - promote the creation of a safe, healthy and high
quality environment in which to live and work.
P2 - promote the strengthening and diversification of the
local economy.
P3 - promote local employment opportunities.
P4 - promote access to education and training.
P5 - promote the meeting of local housing needs.
P5 - involve local communities in the
redevelopment/renewal of the Area.
P7 - promote community cohesion.
Soil
S1 - promote decontamination to international standards
of contaminated soil.
Water
W1 - ensure adequate good quality water supply.
W2 - maintain/improve water quality of waterbodies.
Air/Climate/Noise
C1 - maintain/promote improvement of air quality.
C2 - promote minimisation of greenhouse gas emissions to
the atmosphere.
C3 - reduce trip generation, trip length and the need for
motorised transport.
C4 - promote public transport and attraction of
walking/cycling.
C5 - promote sustainable energy use/generation
C6 - minimise noise pollution.
Cultural Heritage/Material Assets
H1 - safeguard Protected Structures and sites of
archaeological value and maintain environmental
quality of Conservation Areas.
H2 - enhance townscape and general
landscape/environmental quality.
H3 - ensure adequate provision of open space/maintain
and improve access to open space areas.
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7 ASSESSMENT OF MASTER PLAN REVIEW
As noted in Section 2.4, the assessment involved testing for the
following:
(i) The internal compatibility of the Strategic Objectives of the
Master Plan Review were tested against each other, in order
to ensure that no tensions existed between the objectives
that could give rise to conflict.
(ii) The Sustainability Criteria which had been devised were also
tested for compatibility. No tensions were identified and the
exercise is included in Appendix 2 of the report.
(iii) The Strategic Objectives of the Master Plan Review were
tested for compatibility against the Sustainability Criteria.
(iv) Selected policies of the Master Plan Review were tested
against the Sustainability Criteria.
7.1 COMPATIBILITY OF STRATEGIC OBJECTIVES
A set of 14 strategic objectives in Section 1.6 of the Master Plan
Review repeat key socio-economic objectives included in the
1997 Master Plan.
As part of the SEA, the Strategic Objectives were tested for
compatibility with each other (Figure 2). The Objectives were
found to be compatible with a possible uncertain effect between
Objective f (the provision of a wide range of new housing in the
Area in order to achieve a good social mix) and Objective b (the
development of increased opportunities for local employment in
existing and new enterprises in the Area). A modification to the
1997 Master Plan recognised a need for flexibility in the provision
of residential development in areas zoned for industrial use. The
evidence from the land use survey carried out as part of the
Master Plan Review indicates a continual decline in industrial and
warehouse use and its replacement with residential or office use.
Objective i (the improvement of the infrastructure and amenities
of the Area concurrently with or in advance of residential,
commercial and industrial development) and Objective m (the
realisation of the potential of Docklands youth) were found to be
fully compatible. It is envisaged that the latter will be involved in
the proposed Community Greening Initiative.
A key outcome of the carrying out of the compatibility matrix
was the recommendation that an additional Strategic Objective
be included relating to the physical improvement and renewal of
the Area which promotes the physical renewal of the Area to a
high environmental standard, reflecting high quality urban design
and architecture, combined with sustainable energy use.
7.2 COMPATIBILITY OF STRATEGIC OBJECTIVES WITH SUSTAINABILITY CRITERIA
The Strategic Objectives devised as part of the Master Plan
Review were tested for compatibility with the Sustainability
Criteria and were found to be largely compatible (Figure 3).
Some deterioration in environmental quality in terms of
additional noise impacts (Sustainability Criteria C6) will arise in
the course of the improvement of infrastructure in the Area
(Strategy Objective (i)). Additional noise will inevitably be
generated at the construction stage of utility/infrastructure
developments. Equally the expansion of existing opportunities for
local employment (Strategic Objective (b)) could lead to the
generation of additional noise levels. This however is balanced by
the requirement of Strategic Objective (a) to develop a wide
range of sustainable employment opportunities in the Area.
A number of the Strategic Objectives (a, b and d), by virtue of
the fact that they promote development, albeit sustainable
development, are likely to impact in some small way on
greenhouse gas emissions and thus on Sustainability Criteria C2
(promote minimisation of greenhouse gas emissions to the
atmosphere).
The development of increased opportunities for local
employment in existing enterprises (part of Strategic Objective
(b)) creates a possible tension with Sustainability Criteria C5
(promotion of sustainable energy use/generation) and C6
(minimise noise pollution) due to the nature of some existing
local enterprises, particularly those long established workshop and
industrial uses. Such tension is inevitable with some desirable
socio-economic objectives unavoidably having a less than ideal
physical impact, and is balanced by Strategic Objective (a).
Sustainability Criteria C3 (reduce trip generation, trip length and
the need for motorised transport) and C4 (promote public
transport and attraction of walking/cycling) performed well in
the matrix, reflecting the sustainability of redeveloping
brownfield dockland areas. In addition Sustainability Criteria P1
(promote the creation of a safe, healthy and high quality
environment in which to live and work) and P2 (promote the
strengthening and diversification of the local economy) were
found to be fully compatible with all Strategic Objectives.
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STRATEGIC OBJECTIVES COMPATIBILITY
STRATEGIC OBJECTIVES
A. The development of a wide range of sustainable employment opportunities in the Area.
B. The development of increased opportunities for local employment in existing and new enterprisesin the Area.
C. The development of an environment which will attract increased investment and employment intothe Area.
D. The continued development and expansion of the International Financial Services Centre (IFSC) inDocklands.
E. The development of sustainable neighbourhoods with sufficient ‘critical mass’ which will supportservices such as quality public transport, improved retail facilities and other new amenities.
F. The provision of a wide range of new housing in the Area in order to achieve a good social mix.
G. The integration of new residential communities with existing local communities in the Area.
H. The development of sustainable transportation for the Area, the promotion of public transport,walking and cycling (as alternatives to the private car) and improved circulation within the Area.
I. The improvement of the infrastructure and amenities in the Area concurrently with or in advance ofresidential, commercial and industrial development.
J. The development of the amenity, tourism and employment potential of the water bodies in theArea.
K. The identification and development of anchor activities and landmark developments which wouldassist in the regeneration of the Area over the period of the Master Plan.
L. The promotion of increased access to education and training for all residents in the Area.
M. The realisation of the potential of Docklands youth.
N. The renewal of Dublin city as a whole by linking the city centre to Dublin Bay and, in turn, connecting the Docklands Area to the life of the city.
KEY
✓ Compatible
0 No Effect
? Uncertain Effect
X May Conflict
A
✓
✓
✓
✓
✓
✓
✓
✓
✓
✓
✓
✓
✓
B
✓
✓
✓
?
✓
✓
✓
✓
✓
✓
✓
✓
C
✓
✓
✓
✓
✓
✓
✓
✓
✓
✓
✓
D
✓
0
0
✓
✓
✓
✓
✓
✓
✓
E
✓
✓
✓
✓
✓
0
✓
✓
✓
F
✓
0
✓
0
0
0
0
✓
G
0
0
0
0
✓
✓
✓
H
✓
✓
0
0
0
✓
I
✓
✓
0
✓
✓
J
✓
0
✓
✓
K
0
0
✓
L
✓
✓
M
✓ N
FIGURE 2
FIGURE 3
STRATEGIC OBJECTIVESSustainability Criteria
A. The development of a wide range of sustainable employment opportunities in the Area.
B. The development of increased opportunities for local employment in existing and new enterprisesin the Area.
C. The development of an environment which will attract increased investment and employment intothe Area.
D. The continued development and expansion of the International Financial Services Centre (IFSC) inDocklands.
E. The development of sustainable neighbourhoods with sufficient ‘critical mass’ which will supportservices such as quality public transport, improved retail facilities and other new amenities.
F. The provision of a wide range of new housing in the Area in order to achieve a good social mix.
G. The integration of new residential communities with existing local communities in the Area.
H. The development of sustainable transportation for the Area, the promotion of public transport,walking and cycling (as alternatives to the private car) and improved circulation within the Area.
I. The improvement of the infrastructure and amenities in the Area concurrently with or in advanceof residential, commercial and industrial development.
J. The development of the amenity, tourism and employment potential of the water bodies in theArea.
K. The identification and development of anchor activities and landmark developments which wouldassist in the regeneration of the Area over the period of the Master Plan.
L. The promotion of increased access to education and training for all residents in the Area.
M. The realisation of the potential of Docklands youth.
N. The renewal of Dublin city as a whole by linking the city centre to Dublin Bay and, in turn, connecting the Docklands Area to the life of the city.
0 No Significant Effect ? Uncertainty of prediction or knowledge
✓ Beneficial Effect/Likely Beneficial Effect X Some deterioration in environmental quality
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ ✓ ✓ 0 ✓ X ✓ ✓ ✓ ✓ 0 ✓ 0
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ ✓ ✓ 0 ✓ X ✓ ✓ ? ? 0 0 0
✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ ✓ ✓ ✓ ✓ X ✓ ✓ ? ✓ 0 ✓ ✓
✓ ✓ ✓ ✓ 0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 ✓ ✓
0 ✓ ✓ 0 0 ✓ ✓ ✓ ✓ 0 0 0 0 ✓ 0 0 0 0 0 0
0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0 0 0 0 ✓ 0 0 0 0 ✓
0 ✓ ✓ ✓ 0 0 ✓ ✓ 0 0 0 ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0
✓ ✓ ✓ ✓ 0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ X ✓ ✓ ✓
✓ ✓ ✓ ✓ 0 0 ✓ 0 0 0 ✓ ✓ 0 0 0 0 0 ✓ ✓ ✓
0 ✓ ✓ ✓ 0 0 ✓ ✓ 0 0 ✓ ✓ 0 0 0 0 0 0 ✓ ✓
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 0
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 ✓
0 ✓ ✓ ✓ 0 0 0 ✓ 0 0 ✓ 0 0 ✓ ✓ 0 0 0 0 0
APPRAISAL OF STRATEGIC OBJECTIVES
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7.3 COMPATIBILITY OF MASTER PLAN REVIEW POLICIES WITH SUSTAINABILITY CRITERIA
As stated earlier, the policies contained in the Master Plan
Review were tested against the devised Sustainability Criteria by
means of matrices. The completed matrices are illustrated in
Figures 4 to 15. Only the most relevant and important policies
were tested for compatibility. The findings of the exercise are
summarised below.
Social and Community Development Policies (Part 2.2)
Policy Nos. 1, 2 and 3 were tested for compatibility with the
Sustainability Criteria and were found to be compatible (Figure 4).
The development of public transport, as part of the provision of
necessary physical infrastructure infrastructure in the Area will
have a positive impact on a range of Sustainability Criteria
including Criteria C1, C2, C3 and C5.
Economic Development and Employment Policies (Part 2.3)
Policy Nos. 5, 6, 8, 9, 10, 11, 13, 14, 15, 17, 19 and 20 tested
and found to be generally compatible with the Sustainability
Criteria (Figure 5). The matrix points to the need to ensure, in
relation to Policy No. 14 (which seeks to support current
employers in the Area with a view to increasing growth), that
any such growth does not give rise to adverse environmental
impacts.
The continued development and expansion of Dublin Port is
likely to have an impact on air quality/trip generation and will
require assessment (Policy 9). Likewise the possible development
of a sports/leisure stadium at Poolbeg would require the
provision of high quality public transport, to ensure that adverse
environmental impacts are avoided. The noise impacts of any
stadium development would also require assessment (Policy 11).
Education and Training Policies (Part 2.4)
Policy Nos. 1, 6 and 8 were tested. All were found to be
compatible with the Sustainability Criteria (Figure 6).
International Financial Services Policies (Part 3)
Policy Nos. 2 and 5 were tested (Figure 7). The matrix points to
the need to promote sustainable energy use in modern office
developments in order to reduce impact in terms of Sustainability
Criteria C1, C2 and C5. The development of brownfield sites is
fully compatible with Sustainability Criteria C3 and C4.
Introduction – Policy on Mixed Use (Part 4.1)
The Authority’s overarching policy on achieving mixed use
development in the Docklands Area tested very positively against
all Sustainability Criteria (Figure 8), confirming the
appropriateness of pursuing such a policy.
Residential Policies (Part 4.2)
Policy Nos. 1, 3, 4, 8 and 9 were tested and were found to be
compatible with the Sustainability Criteria (Figure 8).
Commuity Facilities Policies (Part 4.3)
Policy Nos. 3 and 4 were tested and were found to be
compatible with the Sustainability Criteria (Figure 8).
Education and Training Policies (Part 4.4)
Policy No. 1 was tested (Figure 9) and was found to be
compatible with the Sustainability Criteria.
Commercial Offices and IFSC Policies (Part 4.5)
Policy Nos. 1 and 3 were tested and pointed to the need to
promote sustainable energy use in modern office buildings
(Figure 9). On the other hand, the development of commercial
offices on brownfield sites performed well in terms of
Sustainability Criteria C3 (reduce trip generation, trip length and
the need for motorised transport) and C4 (promote public
transport and attraction of walking/cycling).
Enterprise, Industry and Utilities Policies (Part 4.6)
Policy Nos. 1, 2, 3, 4, 6 and 7 were tested (Figure 9). Policy No. 2
refers to the retention of suitable areas for small industry and
workshops. The importance of the application of the second
element in the policy, which requires the application of strong
environmental policies, comes through in the matrix. The
environmental impact of any major new projects for heavy
industry on the Poolbeg Peninsula will require careful assessment
(Policy No. 7)
Policy No. 3 encourages the development of facilities which
straddle the description of offices or industry. Again the matrix
points to the need for the promotion of sustainable energy use
in new buildings.
Tourism and Leisure Policies (Part 4.7)
Policy Nos. 1, 6, 9 and 10 were tested and were found to be
compatible with the Sustainability Criteria (Figure 10).
Cultural Uses Policies (Part 4.8)
Policy Nos. 2 and 3 were tested and were found to be
compatible with the Sustainability Criteria (Figure 10).
Retail Policies (Part 4.9)
Policy No. 1 was tested and found to be generally compatible
with the Sustainability Criteria (Figure 10). A possible tension is
indicated with Sustainability Criteria C3 and C5 as the proposed
retail development at The Point may attract additional car traffic
into the Area. This is mitigated by the restriction on the size of
the proposed car park to 700 spaces, including any operational
parking required by The Point Depot.
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Transportation Framework Policies (Part 5.1 )
Policy Nos. 1, 2, 3, 8, 11, 12, 15, 23 and 28 were tested (Figure
11). Policy No. 11, which promotes the provision of public car
parks at key strategic locations including the Point Village, may
have an uncertain impact on Sustainability Criteria C1, C2, C3,
C4, C5 and C6. Any impacts will be mitigated by the size
restriction on the car park at The Point referred to above and the
fact that that car park will cater for short-term parking. The
necessity to have some provision for car parking throughout the
Area in order for renewal/redevelopment to proceed is also
recognised.
Policy No. 23 promotes, in collaboration with Dublin City
Council, the completion of the Environmental Traffic Cell (ETC)
network. Such networks can have very positive impacts on an
area, depending on the boundaries of the ETC. It will be
necessary that ETC boundaries do not split residential
communities to ensure consistency with Sustainability Criteria P7.
Infrastructure Framework Policies (Part 5.2)
Policy Nos. 4 and 5 were tested (Figure 12) and were found to
be compatible with the Sustainability Criteria. A positive impact
on C5 (the promotion of sustainable energy use/generation)
would arise if the Area were to benefit from a Combined Heat
and Power system.
Urban Design and Architecture Policies (Part 6.1)
Policy Nos. 2, 12, 15, 19, 20 and 23 were tested and were found
to be compatible with the Sustainability Criteria (Figure 13).
The need to promote sustainable building design is again an
outcome of the matrix.
Conservation Policies (Part 6.2)
Policy Nos. 6, 7, 9 and 10 were tested and were found to be
compatible with the Sustainability Criteria (Figure 13).
Open Space, Landscaping and Amenity Policies (Part 6.3)
Policy Nos. 1, 2, 3, 4, 8 and 20 were tested and were found to
be compatible with the Sustainability Criteria (Figure 14). Policy
No. 20 requires the Authority to keep under review the potential
to provide a major sporting facility on the Poolbeg Peninsula. The
policy performs very well from a strategic viewpoint in the
matrix, indicating the advantages of a central location for this
type of development.
Financial Requirement Policies (Part 7.2)
Policy Nos. 1, 4 and 5 tested and found to be compatible with
the Sustainability Criteria (Figure 15).
Marketing Docklands (Part 7.3)
Policy No. 2 was tested and found to be compatible with the
Sustainability Criteria (Figure 15).
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FIGURE 4 POLICY APPRAISAL
PART 2.2 SOCIAL AND COMMUNITY DEVELOPMENT
POLICY NO.
Sustainability Criteria
1. forge a partnership with local communities and with the private sector. A high level of participationfrom the local communities is critical to the preparation and implementation of the Master Plan.The Dublin Docklands Development Authority has therefore established a Community LiaisonCommittee (CLC), whose functions are: to maximise the involvement of the communities in thelocal areas in the redevelopment of Docklands; to provide a forum for direct communicationsbetween the Authority, developers and representatives of the local communities and vice versa;and to maximise suitable employment and training opportunities for people from the local areawho are unemployed.
2. promote the development of new housing which will reflect the diversity of needs in anycommunity, including housing for couples with children, housing for single parent families,sheltered housing, and housing for people with disabilities.
3. as a priority, seek to implement the provision of the necessary physical infrastructure in order topromote economic and social development. Such infrastructure is an essential component inattracting investment and in changing the perception of the Area.
0 No Significant Effect ? Uncertainty of prediction or knowledge
✓ Beneficial Effect/Likely Beneficial Effect X Some deterioration in environmental quality
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 ✓
0 ✓ ✓ ✓ 0 ✓ ✓ ✓ 0 0 0 0 0 0 0 0 0 0 ✓ ✓
0 ✓ ✓ ✓ 0 ✓ 0 0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 ✓ ✓
FIGURE 5 POLICY APPRAISAL
PART 2.3ECONOMIC DEVELOPMENT AND EMPLOYMENT
Sustainability Criteria
5. work with the IDA and other state agencies in attracting international services to the Area.6. continue the development of financial services and related business in the
Docklands.8. encourage research and development operations at a number of strategic sites, in co-operation
with the city's universities and third level colleges.9. co-operate with Dublin Port to ensure that the port continues to play its vital national economic
role.
10. promote the clustering of tourism, culture and leisure to develop a significant presence in theDocklands.
11. promote the development of major visitor attractions and leisure initiatives which will generatesignificant movements of Dublin’s citizens into the area.
13. promote community employment projects which create sustainable employment.14. support current employers in the Area with a view to increasing growth.15. identify, with the aid of local communities, job opportunities in small business.17. facilitate the growth of enterprise and business start up in the Area particularly by local residents
through networking and by the provision of advisory services and direction to formal enterpriseservices and resources existing within the city and the state.
19. continue to implement its Local Employment Initiative / Charter through its eleven point actionplan (see Appendix D).
20. priortise the early redevelopment of neglected land areas and amenity schemes to improvethe general perceptions of the Area.
0 No Significant Effect ? Uncertainty of prediction or knowledge
✓ Beneficial Effect/Likely Beneficial Effect X Some deterioration in environmental quality
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ 0 0 ✓ 0 0 0 0 0 0 0 0 0 0 0 0
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 0
0 ✓ ✓ ✓ ✓ 0 0 ✓ 0 0 0 0 0 0 0 0 0 0 0 0
0 ✓ ✓ ✓ ✓ 0 ✓ 0 0 0 ? ? ? ? 0 0 X 0 ? 0
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 ✓ 0 0 0 0 0 0 0 ✓ ✓
0 ✓ ✓ ✓ 0 0 ✓ ✓ 0 0 ✓ 0 0 ? ? 0 ? ✓ ✓ ✓
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 ✓ ✓ ✓ 0 0 0 0
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 ? ? ✓ ✓ 0 0 0 0 0 0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 0
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 ✓ ✓ 0 0 0 0 0
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 ✓ ✓ 0 0 0 0 0
✓ ✓ ✓ ✓ ✓ 0 ✓ ✓ ✓ 0 0 0 0 ✓ ✓ ✓ 0 ✓ ✓ ✓
Part 7 (Final) 3/6/03 11:11 Page 20
21 Dublin Docklands Area Strategic Environmental Assessment of the Draft Master Plan 2003
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FIGURE 6 POLICY APPRAISAL
PART 2.4EDUCATION AND TRAINING
POLICY NO.
Sustainability Criteria
1. encourage and support initiatives designed to reduce educational disadvantage in theDocklands.
6. provide, with the co-operation of FAS,CERT and local schools, job specific training andeducation programmes as the need is identified.
8. seek to ensure that pupils in the Docklands achieve educational success on a par with otherpupils in the Dublin city area by
i) continuing with its educational programmes supplementing existing schools provision, andii) auditing school resources
0 No Significant Effect ? Uncertainty of prediction or knowledge
✓ Beneficial Effect/Likely Beneficial Effect X Some deterioration in environmental quality
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 0
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 0
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 0
FIGURE 7 POLICY APPRAISAL
PART 3INTERNATIONAL FINANCIAL SERVICES
POLICY NO.
Sustainability Criteria
2. promote the development of office accommodation within the Docklands Area in accordance withthe Master Plan to:
" secure the IFSC as a world class city quarter," ensure the long term provision of office/service/housing accommodation to permit sustained
organic growth of the financial services industry within the Docklands. 5. promote the education and training for residents of the Docklands to ensure that job opportunities
in the IFSC are open and accessible to local residents.
0 No Significant Effect ? Uncertainty of prediction or knowledge
✓ Beneficial Effect/Likely Beneficial Effect X Some deterioration in environmental quality
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0 ? ? ✓ ✓ ? 0 0 ✓ ✓
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 0
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FIGURE 8 POLICY APPRAISAL
PART 4.2RESIDENTIAL
Sustainability Criteria
1. promote a significant expansion of the residential base of the Area.3. allocate residential use to all parts of the Area, save those where shared use would be
incompatible with other uses.4. as part of its commitment to the regeneration of the local economy, cater for the development of
social and affordable housing to meet the foreseeable need in this Area, and locate it throughoutthe areas allocated for residential use at a minimum ratio of 20% of all new units.
8. monitor the contemporaneous development or implementation of supporting social and economicfacilities.
9. promote the design of residential complexes which do not articulate social differences.
0 No Significant Effect ? Uncertainty of prediction or knowledge
✓ Beneficial Effect/Likely Beneficial Effect X Some deterioration in environmental quality
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0 0 0 ✓ ✓ ✓ 0 0 ✓ ✓
0 ✓ ✓ ✓ 0 ✓ 0 0 0 0 0 0 0 ✓ ✓ 0 0 0 0 0
0 ✓ ✓ ✓ 0 ✓ ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 0
0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0 0 0 0 0 0 0 0 ✓ ✓
0 ✓ 0 0 0 ✓ ✓ ✓ 0 0 0 0 0 0 0 0 0 0 ✓ 0
PART 4.3COMMUNITY FACILITIES
PART 4.1INTRODUCTION
POLICY NO.
3. seek to identify shortfalls and stimulate initiatives in relation to community infrastructure inconsultation with local communities and fund projects where appropriate through the communityDevelopment Project Initiative.
4. progress the implementation of the Plot 8 community facility in Grand Canal Dock in associationwith community groups and Waterways Ireland.
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 ✓
0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 ✓ 0 0 ✓ ✓ 0 0 ✓ ✓ ✓
1. pursue a policy of mixed use development in the Docklands area which would achieve asustainable environment integrating living, working and leisure.
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 ✓ 0 0 ✓ ✓ ✓ 0 ✓ ✓ ✓
FIGURE 9 POLICY APPRAISAL
PART 4.4EDUCATION AND TRAINING
POLICY NO.
Sustainability Criteria
1. promote the consolidation and renewal of existing primary and secondary level schools in theArea.
0 No Significant Effect ? Uncertainty of prediction or knowledge
✓ Beneficial Effect/Likely Beneficial Effect X Some deterioration in environmental quality
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 0
PART 4.5COMMERCIAL OFFICES AND IFSC
1. provide for the expansion initially of high-quality office building zones from the existing centralbusiness district and locate new office areas around major transport nodes.
3. seek the provision of offices in the Area of different specifications in order to meet marketdemand.
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ 0 0 ✓ 0 0 0 ? ? ✓ ✓ ? 0 0 ✓ ✓
0 ✓ ✓ ✓ ✓ 0 0 ✓ 0 0 0 ? ? ✓ ✓ ? 0 0 ✓ 0
PART 4.6ENTERPRISE, INDUSTRY AND UTILITIES
1. encourage the consolidation and expansion of existing small, medium and large businesseswhere such businesses wish to remain within the Area and are appropriate to the Area.
2. retain suitable areas for small industry and workshop use whilst applying strong environmentalmanagement policies to alleviate any disamenity to neighbouring residential uses.
3. encourage the development of emerging new facilities which straddle the description of offices orindustry in the Docklands and, through its land use strategy, target appropriate lands for suchdevelopment.
4. seek the development of light industry in place of heavy or general industry in appropriatelocations, particularly close to residential and commercial areas.
6. facilitate the consolidation of Dublin Port as a major economic and employment force affectingthe Area.
7. seek to ensure that all future major projects for heavy industry in the Poolbeg Peninsula arecarefully assessed for environmental impacts, particularly as regards emissions and traffic.
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 ✓ ✓ 0 0 0 0 0
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 ✓ ✓ 0 ? 0 0 0
0 ✓ ✓ ✓ ✓ 0 0 ✓ 0 0 0 ? ? ✓ ✓ ? ✓ 0 ✓ 0
0 ✓ ✓ ✓ 0 0 0 ✓ 0 0 0 ✓ 0 ✓ ✓ 0 ✓ 0 0 0
0 ✓ ✓ ✓ ✓ 0 ✓ 0 0 0 ? ? ? ? 0 0 X 0 ? 0
✓ ✓ ✓ ✓ 0 0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 ✓ 0
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23 Dublin Docklands Area Strategic Environmental Assessment of the Draft Master Plan 2003
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FIGURE 10 POLICY APPRAISAL
Sustainability Criteria
1. provide for the development of any major building initiatives by Government which would actas significant tourist entertainment destinations.
6. continue to review the feasibility of providing suitable terminal for cruise liners with DublinPort as the number of visiting ships increases.
9. explore the development of specific tourism projects which will encourage a more substantialtourism footfall in the Docklands.
10. promote leisure and tourism in the water bodies in accordance with the River RegenerationStrategy.
0 No Significant Effect ? Uncertainty of prediction or knowledge
✓ Beneficial Effect/Likely Beneficial Effect X Some deterioration in environmental quality
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 ✓ ✓ ✓ 0 0 ✓ ✓
0 ✓ ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0 ✓ ✓ ✓ 0 0 0 0 0 0 0 0 0 ✓ ✓ ✓ 0 ✓ ✓ ✓
0 ✓ ✓ ✓ 0 0 ✓ ✓ 0 0 ✓ 0 0 0 0 0 0 ✓ ✓ ✓
PART 4.8CULTURAL USES
2. encourage the consolidation or expansion as appropriate of existing cultural facilities.
3. facilitate any Government initiative to locate major cultural centres or buildings in a waterfrontarea of the Docklands as part of a cultural corridor along the Liffey from the IMMA to ThePoint.
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 ✓ ✓ ✓ 0 ✓ ✓ 0
0 ✓ ✓ ✓ 0 0 ✓ ✓ 0 0 0 0 0 ✓ ✓ ✓ 0 ✓ ✓ 0
1. allocate an area for the development of a district centre, the "Point Village", as the easternend of the study area at the East Wall Road close to The Point with suitable off-street carparking.
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ 0 0 0 ✓ 0 0 0 0 0 ? ✓ ? 0 0 ✓ ✓
PART 4.9RETAIL
PART 4.7TOURISM AND LEISURE
POLICY NO.
FIGURE 11 POLICY APPRAISAL
Sustainability Criteria
1. seek the extension of LUAS from Connolly Station to the Point Depot by 2006 and fromHarcourt Street to Guild Street by 2010, in accordance with the timescale outlined in theDTO Strategy 2000-2016.
2. promote the development of the underground Interconnector and Docklands Station withinthe timescale outlined in the DTO Strategy 2000-2016.
3. promote the penetration of commuter bus services into the Area through the extension of theQuality Bus Corridor network on North Wall and Pearse Street with services linking acrossthe Macken Street Bridge, in addition to the extension of city radial routes to the Area, inconsultation with bus operators and the DTO.
8. support the tolling of the Dublin Port Tunnel and the Eastern By-Pass as a trafficmanagement measure and to deter car commuting during the peak period, while facilitatingHGV traffic.
11. promote the provision of public car parks at key strategic locations, including the PointVillage, for short term shopping, leisure and business use with a pricing structure to detercommuter use.
12. appraise, in conjunction with the Dublin Transportation Office, the feasibility of 'park and ride'at strategic locations where the Dublin Port Tunnel/Eastern By-Pass intersects with thequality public transport network, at the edge of the congestion zone.
15. support the provision of a dedicated network of routes for cyclists and pedestriansthroughout the Area.
23. promote, in collaboration with Dublin City Council, a programme of traffic-calming measuresin residential areas and the completion of the network of environmental traffic cells.
28. collaborate with Dublin Port to promote the provision of adequate boating and on-shorefacilities for cruise liners and promote a water bus service.
0 No Significant Effect ? Uncertainty of prediction or knowledge
✓ Beneficial Effect/Likely Beneficial Effect X Some deterioration in environmental quality
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ 0 0 ✓ 0 0 0 ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0
0 ✓ ✓ ✓ ✓ 0 0 ✓ ✓ 0 0 ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0
0 ✓ ✓ ✓ ✓ 0 0 ✓ 0 0 0 ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0
0 ✓ ✓ ✓ 0 0 0 ✓ 0 0 0 0 ✓ ✓ ✓ ✓ ✓ 0 0 0
0 ✓ ✓ ✓ 0 0 0 0 0 0 0 ? ? ? ? ? ? 0 0 0
0 ✓ ✓ ✓ 0 0 0 0 0 0 0 ✓ ✓ ? ✓ ✓ 0 0 0 0
0 ✓ 0 0 ✓ 0 0 ✓ 0 0 0 ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0
0 ✓ 0 0 ✓ 0 0 ? 0 0 0 0 0 0 0 0 0 0 ✓ 0
0 ✓ ✓ ✓ 0 0 ✓ ✓ 0 0 ✓ 0 0 0 ✓ 0 0 0 ✓ ✓
PART 5.1TRANSPORTATION FRAMEWORK
POLICY NO.
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FIGURE 12 POLICY APPRAISAL
Sustainability Criteria
4. keep under review, in co-operation with the ESB and Dublin City Council, the potential ofrecovery and distribution of waste heat from the Poolbeg Power Station and any Waste toEnergy Plant which may be developed and consider the possibilities for Combined Heat andPower facilities, as part of an overall energy conservation programme for the Area.
5. review community needs and promote a range of environmental and physical improvements inconsultation with local communities.
0 No Significant Effect ? Uncertainty of prediction or knowledge
✓ Beneficial Effect/Likely Beneficial Effect X Some deterioration in environmental quality
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ 0 0 0 0 0 0 0 0 ✓ ✓ 0 0 ✓ 0 0 0 0
0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 0 0 0 0 ✓ ✓ ✓
PART 5.2INFRASTRUCTURE FRAMEWORK
POLICY NO.
FIGURE 13 POLICY APPRAISAL
Sustainability Criteria
2. seek to maintain the variety and diversity in the environmental character of the many areasthat make up the Docklands.
12. seek to encourage closer links north and south, both psychologically and physically, byencouraging further bridge links.
15. seek to conserve the existing street pattern where appropriate.
19. reinforce the pattern of existing pedestrian movement throughout the Area in both the east-west and north-south direction, with improved north-south movements through the provisionof the aforementioned cross-river links.
20. promote high standards of design and construction in building works for which it is directlyresponsible and where control can be exercised through the Authority's planning powers inareas selected under Section 25 of the Act.
23. promote the enhancement of streetscapes to create safe streets and secure environments.
0 No Significant Effect ? Uncertainty of prediction or knowledge
✓ Beneficial Effect/Likely Beneficial Effect X Some deterioration in environmental quality
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
✓ ✓ ✓ 0 0 0 ✓ ✓ 0 0 0 0 0 0 0 0 0 ✓ ✓ ✓
0 ✓ ✓ ✓ ✓ 0 0 ✓ 0 0 0 0 0 ✓ ✓ ✓ 0 ✓ ✓ 0
0 ✓ 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ✓ ✓ ✓
0 ✓ 0 0 0 0 0 ✓ 0 0 0 0 0 ✓ ✓ 0 0 0 0 0
0 ✓ 0 0 0 0 0 0 0 0 0 ✓ ✓ 0 0 ✓ 0 ✓ ✓ 0
0 ✓ 0 0 0 0 0 ✓ 0 0 0 0 0 0 0 0 0 ✓ ✓ ✓
PART 6.1URBAN DESIGN AND ARCHITECTURE
POLICY NO.
6. preserve protected structures and sites of historical architectural or artistic interest whichcontribute to the character of the Area.
7. encourage the rehabilitation, renovation and re-use of older buildings where appropriate andin line with its policy on sustainability.
9. encourage, where appropriate, the retention of buildings, features or structures which aresignificant in terms of local character or community identity.
10. ensure the sites identified as being of possible interest in the Zone of Archaeological Interestand in the Inventory of Industrial Archaeology are fully investigated and recorded, whereappropriate, before development is undertaken.
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ✓ ✓ 0
0 ✓ 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ✓ ✓ 0
0 ✓ 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ✓ ✓ 0
0 ✓ 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ✓ ✓ 0
PART 6.2CONSERVATION
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FIGURE 14 POLICY APPRAISAL
Sustainability Criteria
1. seek to establish the Eco Park on the Poolbeg Peninsula.
2. seek to incorporate a major new public open space at the confluence of the Royal Canaland the Liffey while facilitating any Government initiative to locate the National ConferenceCentre or a major cultural building on the site.
3. develop the entire of the Liffey campshires as public promenades and cycle ways.
4. seek the development of a significant linear park suitable for active and passive recreationand incorporating cycle and pedestrian routes along the Royal Canal.
8. maximise the amenity potential of the water bodies, in accordance with the Authority's 'RiverLiffey Regeneration Strategy'.
20. keep under review the potential to provide a major sporting facility on the PoolbegPeninsula.
0 No Significant Effect ? Uncertainty of prediction or knowledge
✓ Beneficial Effect/Likely Beneficial Effect X Some deterioration in environmental quality
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
✓ ✓ 0 0 ✓ 0 ✓ ✓ 0 0 0 0 0 0 0 0 0 0 ✓ ✓
0 ✓ 0 0 0 0 0 ✓ 0 0 0 0 0 0 0 0 0 0 ✓ ✓
0 ✓ 0 0 0 0 0 ✓ 0 0 0 0 0 0 ✓ 0 0 ✓ ✓ ✓
0 ✓ 0 0 0 0 0 ✓ 0 0 0 0 0 0 ✓ 0 0 ✓ ✓ ✓
0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 ✓ 0 0 0 0 0 0 ✓ ✓ ✓
0 ✓ ✓ ✓ ✓ 0 0 ✓ ✓ 0 0 ✓ ✓ ✓ ✓ ✓ 0 0 ✓ ✓
PART 6.3OPEN SPACE, LANDSCAPING AND AMENITY
POLICY NO.
FIGURE 15 POLICY APPRAISAL
PART 7.2FINANCIAL REQUIREMENTS
POLICY NO.
Sustainability Criteria
1. reinvest gains in the Area.
4. examine the potential for new sources and methods of funding including Public PrivatePartnerships.
5. seek to maximise the allocation of EU funding to the Area.
0 No Significant Effect ? Uncertainty of prediction or knowledge
✓ Beneficial Effect/Likely Beneficial Effect X Some deterioration in environmental quality
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 0
0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 0
0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 ✓ 0 0 0 0 0 0 0 0 0
PART 7.4MARKETING
2. seek the support and involvement of the community in promoting its marketing strategy.
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ ✓ 0 0 ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 0
Part 7 (Final) 3/6/03 11:11 Page 25
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8 MITIGATION
The mitigation measures or key recommendations arising from
the SEA exercise are as follows:
1. Include an additional Strategic Objective relating to the
physical improvement/renewal of the Area. This is not covered
by existing objectives and is an important remit of the
Authority. A suggested wording would be that the Authority
will “promote the sustainable physical renewal of the Area to
a high environmental standard, reflecting high quality urban
design and architecture, combined with efficient energy use”.
2. Include additional policies as follows in the appropriate
sections of the Master Plan Review:
(i) A policy on Seveso 11 activities. Directive 96/82/EC relates
to the control of major accidents involving dangerous
substances. Some activities covered by the Directive are
located in the Docklands Area. It is considered that the
Master Plan Review should include a policy in relation to
the location and control of such activities.
(ii) A policy on catering for rising flood levels arising from
global warming. This has implications in terms of minimum
ground floor levels for new development in the Area.
3. Policy No. 14 of Part 2.3 Economic Development and
Employment states that the Authority will support current
employers in the area with a view to increasing growth. It is
recommended that the policy be qualified by the addition of
the wording “while applying strong environmental
management policies to alleviate any disamenities which
could arise”.
4. There are two separate, but related, policies in the Master
Plan Review regarding Dublin Port (Policy No.9, Economic
Development and Employment and Policy No. 6, Enterprise,
Industry and Utilities). It is recommended that they be
combined in one policy for the purpose of clarity.
5. It is recommended that Policy No. 8, IFSC, which seeks seek
the provision of offices in the Area of different specifications
in order to meet market demand, be moved to the policy
section on Commercial Offices, which is considered more
suitable.
6. Residential Policy No.10 states that the Authority will
“promote conditions and formulate incentives that will render
Docklands an attractive location in which to start and/or raise
a family”. It may be that the Authority will be in a position to
promote rather than to formulate incentives. Consideration
should be given to rewording the policy.
7. It is recommended that Policy Nos. 15 and 16, Transportation
Framework be rearranged and that the first part of Policy No.
16, which refers to the creation of a safe environment for
pedestrians, cyclists and vehicles, be incorporated into Policy
No 15. leaving a distinct separate policy relating to the
Sandycove to Sutton proposal.
8. It is considered that Policy No. 5, Infrastructure Framework,
which seek to review community needs and promote a range
of environmental and physical improvements in consultation
with local communities, should be moved to Policies on Social
and Community Development.
9. It is recommended that Policy No. 20, Urban Design and
Architecture, be expanded to make reference to sustainable
design and that the revised policy, in order to stress its
importance, become Policy No. 1.
10.There is an overlap between Policy Nos. 17 and 23, Urban
Design and Architecture. These policies could be combined.
11.Policy No. 7, Conservation refers to the Authority’s policy on
sustainability. It is recommended that the policy refer instead
to the proposed additional Strategic Objective referred to
above.
12.Policy No.11, Conservation may require clarification. It is
unclear whether the Authority itself intends using fiscal
incentives to achieve conservation and environmental
objectives or whether it will promote the use of such
incentives. Consideration should be given to the substitution
of the wording ‘promote the use of’ for ‘use’ in the policy.
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27 Dublin Docklands Area Strategic Environmental Assessment of the Draft Master Plan 2003
9 MONITORING
Article 10 of the SEA Directive requires Member States to monitor
the significant environmental effects of the implementation of
plans and programmes in order to identify at an early stage
unforeseen adverse effects, and to be able to undertake
appropriate remedial action. Section 7.1 of the Master Plan
Review sets out the Authority’s proposals for monitoring. As part
of the monitoring process, it is proposed to prepare an annual
monitoring report on the implementation of the Master Plan.
As indicated in the Master Plan Review, some indicators do not
lend themselves to annual monitoring. The Authority will also
co-operate with the relevant agencies in monitoring the
environmental impacts of the Master Plan. The Review
incorporates two additional policies in respect of
monitoring which require the Authority to:
(iii) undertake appropriate survey work and collection of data to
ensure effective ongoing monitoring of the implementation
of the Plan; and
(iv) co-operate with Dublin City Council, the Environmental
Protection Agency and other agencies, to ensure that the
environmental impacts of the Plan are monitored in
accordance with Department of the Environment and Local
Government guidelines and/or Strategic Environmental
Assessment (SEA) Regulations.
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10 OVERALL FINDINGS FROM THE ASSESSMENT
It is clear from the assessment of the Strategic Objectives and
Policies of the Master Plan Review that the Review has a strong
sustainable thrust and focus. Almost all objectives and policies
were found to be either compatible or not in conflict with the
Sustainability Criteria devised for the assessment exercise. No
conflicting objectives or policies were evident. The exercise
confirms that the Master Plan Review is a robust, focussed and
clearly thought out document that will continue to provide a
positive strategic framework for the development of the
Docklands Area. This is borne out by the mitigation measures
arising from the exercise in Section 8.0 above, which can only be
described as minor in nature. The mitigation measures essentially
remove some duplication, clarify a number of policies and make
good a few policy omissions.
Inevitably with a Plan of this nature, which covers a centrally
located, former dockland area with a wide variety of uses and
amenity areas, tensions are thrown up by some of the proposed
policies. In particular these tensions arise in relation to policies
which seek to consolidate/ expand existing industrial or port use.
There are valid socio-economic reasons for the inclusion of such
policies. Such tensions cannot be avoided and are mitigated by
the requirement to avoid any adverse environmental impacts.
The possibility of the development of a major sports facility on
the Poolbeg Peninsula performs well in the assessment, pointing
to the suitability of a central location for such a facility. It would
be essential to provide high quality public transport to serve a
development of this nature in order to avoid a negative impact
on the area.
The need to incorporate sustainable design into modern office
developments, in order to reduce energy demand and also
contribute to meeting Ireland’s obligations to greenhouse gas
emissions under the Kyoto Protocol, is also evident from the
assessment. This is a wider issue, with market forces playing a
dominant role, but is one which the Authority may bear in mind
in assessing proposals for development.
10
OV
ERA
LL F
IND
ING
SFR
OM
TH
E A
SSES
SMEN
T
Part 10 (Final) 30/5/03 13:08 Page 28
29 Dublin Docklands Area Strategic Environmental Assessment of the Draft Master Plan 2003
APPENDIX I
Consultees on the Issues to be Covered by the SEA
Department of the Environment and Local Government
Department of Arts, Heritage, Gaeltacht and the Islands
Department of Marine, Communications & Natural Resources
Department of Education and Science
Dúchas
Dublin City Council
Dublin Port Company
Railway Procurement Agency
National Roads Authority
Bord Failte
Environmental Protection Agency
The Heritage Council
The Arts Council
Forfás
Dublin Transportation Office
Electricity Supply Board
Bord Gais
Waterways Ireland
Office of the Strategic Planning Guidelines for
the Greater Dublin Area
An Taisce
Irish Planning Institute
Royal Town Planning Institute
RIAI
Institute of Engineers of Ireland
Society of Chartered Surveyors
APP
END
IX I
xAppendix 1 (Final) 30/5/03 13:09 Page 29
30
APP
END
IX II
APPENDIX 2 POLICY APPRAISAL
SUSTAINABILITY CRITERIA Sustainability Criteria
Bio diversity/Flora and Fauna
B1 - safeguard designated areas / areas of nature conservation importance while increasing potential for wildlife/flora and fauna, where appropriate.
Population
P1 - promote the creation of a safe, healthy and high quality environment in which to live and work.
P2 - promote the strengthening and diversification of the local economy.
P3 - promote local employment opportunities.
P4 - promote access to education and training
P5 - promote the meeting of local housing needs
P6 - involve local communities in the redevelopment/renewal of the Area
P7 - promote community cohesion.
Soil
S1 - promote decontamination to international standards of contaminated soil.
Water
W1 - ensure adequate good quality water supply
W2 - maintain/improve water quality of waterbodies.
0 No Link ? Compatibility uncertain
✓ Compatible X May conflict
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
✓ ✓ ✓ ✓ 0 ✓ ✓ 0 0 ✓ 0 0 0 0 0 0 0 ✓ ✓
✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓
✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓
✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0 0 0 ✓ ✓ 0 0 0 0 0✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0 0 0 ✓ ✓ 0 0 0 0 ✓
✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 ✓ 0 0 0 0 0 ✓ 0 0 0 ✓
✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 ✓
0 ✓ ✓ ✓ ✓ ✓ ✓ 0 0 0 0 0 0 0 0 0 0 0 ✓
0 ✓ ✓ 0 0 0 0 0 0 ✓ 0 0 0 0 0 0 0 ✓ 0
0 ✓ ✓ ✓ 0 ✓ 0 0 0 ✓ 0 0 0 0 0 0 0 ✓ 0✓ ✓ ✓ ✓ ✓ 0 ✓ ✓ ✓ ✓ 0 0 0 0 0 0 ✓ ✓ ✓
POLICY APPRAISAL
SUSTAINABILITY CRITERIA Sustainability Criteria
Air/Climate/Noise
C1 - maintain/promote improvement of air quality
C2 - promote minimisation of greenhouse gas emissions to the atmosphere
C3 - reduce trip generation, trip length and the need for motorised transport
C4 - promote public transport and attraction of walking/cycling
C5 - promote sustainable energy use/generation
C6 - minimise noise pollution
Cultural Heritage/Material Assets
H1 - safeguard Protected Structures and sites of archaeological value and maintainenvironmental quality of Conservation Areas
H2 - enhance townscape and general landscape/environmental quality
H3 - ensure adequate provision of open space/maintain and improve access to open space areas.
0 No Link ? Compatibility uncertain
✓ Compatible X May conflict
KEY
B1 P1 P2 P3 P4 P5 P6 P7 S1 W1 W2 C1 C2 C3 C4 C5 C6 H1 H2 H3
0 ✓ ✓ 0 0 0 0 0 0 0 0 ✓ ✓ ✓ ✓ 0 ✓ ✓ 00 ✓ ✓ 0 0 0 0 0 0 0 0 ✓ ✓ ✓ ✓ 0 0 ✓ 00 ✓ ✓ ✓ ✓ 0 0 0 0 0 0 ✓ ✓ ✓ ✓ ✓ 0 ✓ ✓
0 ✓ ✓ ✓ ✓ 0 0 0 0 0 0 ✓ ✓ ✓ ✓ ✓ 0 ✓ ✓
0 ✓ ✓ 0 0 ✓ 0 0 0 0 0 ✓ ✓ ✓ ✓ 0 0 0 00 ✓ ✓ 0 0 0 0 0 0 0 0 0 0 ✓ ✓ 0 0 ✓ 0
0 ✓ ✓ 0 0 0 0 0 0 0 ✓ ✓ 0 0 0 0 0 ✓ ✓
✓ ✓ ✓ 0 0 0 0 0 ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 ✓ ✓ ✓
✓ ✓ ✓ ✓ ✓ ✓ ✓ ✓ 0 0 ✓ 0 0 ✓ ✓ 0 0 ✓ ✓
APPENDIX II
xAppendix 1 (Final) 30/5/03 13:09 Page 30
31 Dublin Docklands Area Strategic Environmental Assessment of the Draft Master Plan 2003
BIBLIOGRAPHYBrady Shipman Martin et. al., 1999, Strategic Planning
Guidelines for the Greater Dublin Area.
Department of the Environment, 1997, Sustainable Development
– A Strategy for Ireland.
Department of the Environment, 2000, National Climate Change
Strategy.
Department of the Environment and Local Government, 1999,
Residential Density Guidelines for Planning Authorities.
Department of the Environment and Local Government, 2000,
Retail Planning Guidelines for Planning Authorities.
DTZ Pieda Consulting et al, 2001, Retail Planning Strategy for the
Greater Dublin Area.
Dublin Corporation, 1999, Dublin City Development Plan.
Dublin Docklands Development Authority, 1997, Dublin
Docklands Area Master Plan.
Dublin Docklands Development Authority, 2000, Environmental
Impact Statement of Development Proposals contained in the
Planning Scheme for the Grand Canal Dock Area.
Dublin Docklands Development Authority, 2001, Environmental
Impact Statement of Development Proposals contained in the
Planning Scheme for Docklands North Lotts.
Dublin Transportation Office, 2002, A Platform for Change,
Strategy 2000 to 2016.
Environmental Protection Agency, 2000, The Water Quality of
Rivers and Streams.
Environmental Protection Agency, 2000, Air Quality and
Monitoring, Annual Report 2000.
Natural Environment Consultants Ltd., 2000, Report to the
Authority on Nature Conservation and the Poolbeg Peninsula.
Office of the Deputy Prime Minister, 2002, Draft Guidance on
the Strategic Environmental Assessment Directive.
The Economic and Social Research Institute, 2000, The
Employment and Socio-Demographic Profile of the Dublin
Docklands Area.
BIBL
IOG
RAPH
Y
xxBibliography (Final) 30/5/03 13:10 Page 31
Údarás Forbartha Dugthailte Baile Átha CliathDublin Docklands Development Authority
Cé Theach an Chustaim, Baile Átha Cliath 1Custom House Quay, Dublin 1, Ireland
t: +353 1 818 3300 f: +353 1 818 3399 e: [email protected] w: www.ddda.ie
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