Introduction To Environmental Impact Assessment

Höfundur John Glasson; Riki Therivel

Útgefandi Taylor & Francis

Snið ePub

Print ISBN 9781138600744

Útgáfa 5

Útgáfuár 2019

7.890 kr.

Description

Efnisyfirlit

  • Cover
  • Half Title
  • Series Information
  • Title Page
  • Copyright Page
  • Contents
  • Preface to the first edition
  • Preface to the fifth edition
  • Acknowledgements
  • Part 1 Principles and procedures
  • 1 Introduction and principles
  • 1.1 Introduction
  • 1.2 The nature of environmental impact assessment
  • 1.2.1 Definitions
  • 1.2.2 Environmental impact assessment: a process
  • 1.2.3 Environmental impact statements: the documentation
  • 1.3 The purposes of environmental impact assessment
  • 1.3.1 An aid to decision-making
  • 1.3.2 An aid to the formulation of development actions
  • 1.3.3 A vehicle for stakeholder consultation and participation
  • 1.3.4 An instrument for sustainable development
  • The nature of sustainable development
  • Institutional responses to sustainable development
  • 1.4 Projects, environment and impacts
  • 1.4.1 The nature of major projects
  • 1.4.2 Dimensions of the environment
  • 1.4.3 The nature of impacts
  • 1.5 Key participants in the EIA process
  • 1.6 Evolving perspectives on EIA
  • 1.6.1 EIA in its theoretical context
  • 1.6.2 The importance of adaptive EIA
  • 1.6.3 EIA in a rapidly growing impact assessment (IA) family
  • Scope
  • Scale
  • Integration
  • 1.7 Current issues in environmental impact assessment
  • 1.7.1 The nature of methods of assessment
  • 1.7.2 The relative roles of participants in the process
  • 1.7.3 The quality and effectiveness of EIA
  • 1.7.4 The quality, efficiency and proportionate nature of the EIA process
  • 1.7.5 Beyond the decision
  • 1.7.6 Managing the widening scope and complexity of IA activity
  • 1.8 An outline of subsequent parts and chapters
  • Some questions 1
  • References
  • 2 US origins and worldwide development
  • 2.1 Introduction
  • 2.2 The National Environmental Policy Act and subsequent US systems
  • 2.2.1 Legislative history
  • 2.2.2 An interpretation of NEPA
  • 2.2.3 A summary of NEPA procedures
  • 2.2.4 Recent trends in EIS activity
  • 2.2.5 Little NEPAs and the case of California
  • 2.3 NEPA critique, review and changes
  • 2.3.1 Strengths and weaknesses
  • 2.3.2 System review
  • 2.3.3 Important amendments
  • 2.3.4 Streamlining, synchronizing and integrating
  • 2.4 The worldwide spread of EIA
  • 2.4.1 Rapid evolution of EIA systems worldwide
  • 2.4.2 System variations and trends
  • 2.5 International bodies and EIA procedures
  • 2.6 Summary
  • Some questions 2
  • Notes
  • References
  • 3 EU and UK agency and legislative contexts
  • 3.1 Introduction
  • 3.2 EC Directive 85/337
  • 3.2.1 Legislative history
  • 3.2.2 Summary of EC Directive 85/337 procedures
  • 3.3 EC Directive – ongoing issues and reviews
  • 3.3.1 Divergent practice in a converging system?
  • 3.3.2 Reviews and amendments 1993 to 2009
  • 1993 review; 1997 amendments and subsequent review
  • The 2003 review of the amended Directive 97/11/EC and further amendments
  • 2009 review and 2011 amendments/consolidation of Directive (2011/92/EU)
  • 3.4 Current EIA Directive (2014/52/EU)
  • 3.4.1 Genesis of the revised EIA Directive
  • 3.4.2 Main changes in the revised EIA Directive (2014/52/EU)
  • 3.4.3 Detailing specific changes
  • 3.5 UK development of EIA
  • 3.5.1 Limitations of the land-use planning system
  • 3.5.2 North Sea oil- and gas-related EIA initiatives
  • 3.5.3 Department of the Environment scepticism
  • 3.6 UK EIA regulations and agencies – an overview
  • 3.6.1 UK EIA regulations: an overview
  • 3.6.2 The principal actors in the UK EIA system
  • 3.7 The Town and Country Planning (Environmental Impact Assessment) Regulations 2017
  • 3.7.1 Screening – which projects require EIA?
  • 3.7.2 The contents of the EIA
  • 3.7.3 Statutory and other consultees
  • 3.7.4 Carrying out the EIA; preparing the EIS
  • 3.7.5 Submitting the EIS and planning application: public consultation (see Figure 3.3)
  • 3.7.6 Planning decision (Figure 3.3)
  • 3.8 Infrastructure Planning (EIA) Regulations 2017 (HMG 2017)
  • 3.9 Summary
  • Some questions 3
  • Notes
  • References
  • Part 2 Process
  • 4 Starting up: early stages
  • 4.1 Introduction
  • 4.2 Managing the EIA process
  • 4.2.1 The EIA team
  • 4.2.2 The style of the EIA process
  • 4.2.3 EIA costs and resources
  • 4.3 Project screening – is an EIA needed?
  • 4.4 Scoping – which impacts and issues to consider?
  • 4.5 The consideration of alternatives
  • 4.5.1 Regulatory requirements
  • 4.5.2 Identification of reasonable alternatives
  • 4.5.3 Assessment and comparison of alternatives
  • 4.5.4 Explanation of the choice of preferred alternative
  • 4.6 Understanding the project/development action
  • 4.6.1 Understanding the dimensions of the project
  • 4.6.2 Sources and presentation of data
  • 4.7 Establishing the environmental baseline
  • 4.7.1 General considerations
  • 4.7.2 Sources and presentation of data
  • 4.8 Impact identification
  • 4.8.1 Checklists
  • 4.8.2 Matrices
  • 4.8.3 Networks or causal chain analyses
  • 4.8.4 Overlay (or constraints) maps
  • 4.8.5 Summary of identification methods
  • 4.9 Summary
  • Some questions 4
  • Note
  • References
  • 5 Impact prediction, evaluation, mitigation and enhancement
  • 5.1 Introduction
  • 5.2 Prediction
  • 5.2.1 Dimensions of prediction (what to predict)
  • 5.2.2 Methods and models for prediction (how to predict)
  • Mathematical and computer-based models
  • Physical/architectural models and computer graphics
  • Expert judgements and analogue models
  • Other methods for prediction
  • Choice of prediction methods
  • Causal networks in EIA prediction
  • 5.2.3 Living with uncertainty
  • The nature of uncertainty, uncertainty in EIA and uncertainty disclosure
  • Handling uncertainty
  • 5.2.4 Some current data forecasting sources
  • 5.3 Evaluation and assessing significance
  • 5.3.1 Evaluation in the EIA process – the determination of significance
  • The importance of significance
  • Frameworks for determining significance
  • Criteria and standards for determining significance thresholds
  • Range of methods for assessing significance
  • 5.3.2 Cost–benefit analysis and monetary valuation techniques
  • 5.3.3 Scoring, weighting and multicriteria methods
  • 5.4 Mitigation and enhancement
  • 5.4.1 The nature of mitigation measures and the mitigation hierarchy
  • 5.4.2 Mitigation in the EIA process
  • 5.4.3 Enhancement of potential benefits
  • Nature and importance of enhancement
  • Enhancement examples
  • Community Benefits Agreements
  • 5.4.4 Trading off impacts
  • 5.5 Summary
  • Some questions 5
  • References
  • 6 Participation, presentation and review
  • 6.1 Introduction
  • 6.2 Public consultation and participation
  • 6.2.1 What is public participation?
  • 6.2.2 Advantages and disadvantages of public participation
  • 6.2.3 Requirements and methods for effective participation
  • 6.2.4 EU procedures
  • 6.3 Consultation with statutory consultees and other countries
  • 6.4 EIA presentation
  • 6.4.1 Contents and organization
  • 6.4.2 Clarity of communication
  • 6.4.3 Presentation
  • 6.5 Review of EISs
  • 6.6 Decisions on projects
  • 6.6.1 EIA and project authorization
  • 6.6.2 EIA and public inquiries
  • 6.6.3 Challenging a decision: judicial review
  • 6.6.4 Challenging a decision: the European Commission
  • 6.7 Summary
  • Some questions 6
  • Notes
  • References
  • 7 Monitoring and auditing: after the decision
  • 7.1 Introduction
  • 7.2 The importance of monitoring and auditing in the EIA process
  • 7.3 Some key questions for monitoring and auditing in EIA
  • 7.3.1 What, how, by whom and where?
  • 7.3.2 Mandatory or discretionary?
  • 7.4 Some international monitoring practice
  • 7.4.1 USA – NEPA, and the specific case of California
  • 7.4.2 The case of Hong Kong
  • 7.4.3 UK experience
  • 7.4.4 Some developing countries’ experiences
  • 7.5 Auditing in practice
  • 7.6 A UK case study: monitoring and auditing the local socio-economic impacts of the Sizewell B PWR construction project
  • 7.6.1 Background to the case study
  • 7.6.2 Operational characteristics of the monitoring study
  • 7.6.3 Some findings from the studies
  • Employment
  • Local economy
  • Housing
  • Traffic and noise
  • Crime
  • Residents’ perceptions
  • 7.6.4 Learning from monitoring: Sizewell B and Sizewell C
  • 7.7 A UK case study: monitoring the local impacts of the London 2012 Olympics project
  • 7.7.1 Nature of the project and its impacts life cycle
  • 7.7.2 Construction stage monitoring
  • 7.8 Summary
  • Some questions 7
  • References
  • Part 3 Practice
  • 8 UK practice
  • 8.1 Introduction
  • 8.2 EIA activity – number and type of EISs and projects
  • 8.2.1 Mainstream regulations
  • Number and broad location of EISs
  • Types of projects
  • Sources of EISs
  • 8.2.2 The particular case of NSIPs/major projects
  • 8.3 A SWOT analysis overview of UK EIA practice
  • 8.4 Particular features of UK EIA practice
  • 8.4.1 Pre-submission – screening and scoping
  • Screening
  • Scoping and pre-submission consultation
  • 8.4.2 Submission – EIS quality
  • Studies of EIS quality
  • Determinants of EIS quality
  • 8.4.3 The post-submission EIA process
  • Review
  • Consultation and public participation
  • Decision-making
  • 8.5 Legal challenges – UK and EU
  • 8.6 Costs and benefits of EIA
  • 8.6.1 Costs of EIA
  • 8.6.2 Benefits of EIA
  • 8.7 Some case studies in UK EIA practice
  • 8.7.1 Public participation – Portsmouth incinerator project
  • Context
  • Background to the proposed scheme
  • The two-stage participation approach
  • Evaluation of the process
  • Summary
  • 8.7.2 Mitigation and enhancement – Hinkley Point C new nuclear project
  • The project
  • Predicted scale of in-migrant construction stage workforce
  • Managing traffic impacts – mitigation and enhancement
  • Managing accommodation impacts – mitigation and enhancement
  • Summary and project local legacy impacts
  • 8.7.3 Cumulative impacts – ornithological impacts of North Sea offshore wind farms
  • UK offshore wind farm under construction
  • Assessing cumulative impacts on North Sea ornithology
  • Approaches to mitigation
  • Summary and cumulative assessment issues
  • 8.7.4 Potential trade-offs for a controversial project – Heathrow Runway 3
  • Context
  • Trade-off issues (as reported by the national press)
  • 8.8 Summary
  • Some questions 8
  • References
  • 9 EIA practice worldwide
  • 9.1 Introduction
  • 9.2 Africa and the Middle East
  • 9.2.1 Overview
  • 9.2.2 Example: Benin
  • 9.3 Asia
  • 9.3.1 Overview
  • 9.3.2 Example: China
  • 9.4 Central and South America
  • 9.4.1 Overview
  • 9.4.2 Example: Peru
  • 9.5 Central and Eastern Europe
  • 9.5.1 Overview
  • 9.5.2 Example: Latvia
  • 9.6 Oceania
  • 9.6.1 Overview
  • 9.6.2 Example: Western Australia
  • 9.7 Small island developing states
  • 9.8 Marine areas and areas beyond national jurisdictions
  • 9.9 Disasters
  • 9.10 Summary
  • Some questions
  • References
  • Part 4 Prospects
  • 10 EIA impact areas, current and emerging
  • 10.1 Introduction
  • 10.2 EIA topic areas
  • 10.3 Biophysical impacts
  • 10.3.1 Water
  • 10.3.2 Soils, land and geology
  • 10.3.3 Air
  • 10.3.4 Flora, fauna and biodiversity
  • 10.3.5 Noise
  • 10.3.6 Transport
  • 10.3.7 Landscape and visual
  • 10.4 Socio-economic impacts
  • 10.4.1 Economic
  • 10.4.2 Social
  • 10.4.3 Health
  • 10.5 Emerging impact areas
  • 10.5.1 Equality/deprivation
  • 10.5.2 Culture and language
  • 10.5.3 Land acquisition, resettlement and livelihoods
  • 10.5.4 Climate change
  • 10.5.5 Ecosystem services
  • 10.6 Wider impact considerations
  • 10.6.1 Risk
  • 10.6.2 Resilience
  • 10.6.3 Cumulative impacts
  • 10.7 Summary
  • Some questions
  • References
  • 11 EIA next steps: the effectiveness and efficiency of the process
  • 11.1 Introduction
  • 11.2 EIA effectiveness
  • 11.2.1 What is effectiveness?
  • 11.2.2 EIA effectiveness studies
  • 11.3 A more proportionate EIA
  • 11.3.1 What is disproportionate about EIA?
  • 11.3.2 How can we deliver a more proportionate EIA? Some international examples
  • 11.3.3 Are there dangers in this approach?
  • 11.4 Technological change and EIA
  • 11.4.1 Remote sensing and better baselines
  • 11.4.2 Expanding roles for the public and social media
  • 11.4.3 Big data
  • 11.4.4 Data visualization
  • 11.4.5 Expert systems and decision support systems
  • 11.5 Changing interpretation of the ‘project’: new types, project splitting, ‘in principle’ projects, environmental impact design, and demolition and decommissioning
  • 11.5.1 New project types and sectors
  • 11.5.2 Salami slicing
  • 11.5.3 ‘In principle’ projects
  • 11.5.4 Project design and environmental limits
  • 11.5.5 Decommissioning
  • 11.6 Links to project implementation and adaptive management via EMS and EMPs
  • 11.6.1 Context: the assessment–implementation gap
  • 11.6.2 Environmental management systems (EMS)
  • 11.6.3 Environmental management plans (EMPs)
  • 11.6.4 An evolving and divergent management practice
  • 11.7 Towards integrated assessment
  • 11.8 Conclusions
  • Some questions
  • References
  • 12 Widening the scope: strategic environmental assessment
  • 12.1 Introduction
  • 12.2 Strategic environmental assessment (SEA)
  • 12.2.1 Definitions
  • 12.2.2 The need for SEA
  • 12.2.3 Problems with SEA
  • 12.3 SEA worldwide
  • 12.3.1 The USA
  • 12.3.2 European Union and UNECE
  • 12.3.3 England
  • 12.3.4 China
  • 12.4 SEA effectiveness
  • 12.5 Summary
  • Some questions
  • References
  • Appendix 1: The text of EC EIA Directive 2014/52/EU
  • Appendix 2: Town and Country Planning (EIA) Regulations 2017
  • Appendix 3: Environmental Impact Statement (EIS) review package (IAU, Oxford Brookes University)
  • Index
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