AN INTRODUCTION TO CUMULATIVE EFFECTS ASSESSMENT.

Slides:



Advertisements
Similar presentations
Identify Problems, Planning Objectives and Constraints.
Advertisements

Lesson 3 ODOT Analysis & Assessment. Analysis & Assessment Learning Outcomes As part of a small group, apply the two- part analysis by generating exposure-
Jeopardy Changing Landscape Using Resources Biodiver- sity Challenges Miscellan- eous Q $100 Q $200 Q $300 Q $400 Q $500 Q $100 Q $200 Q $300 Q $400 Q.
Presented to: 2010 Airports Conference By: Sue McDonald With slides by Tom Klin, CH2M HILL Date: March 3, 2010 Federal Aviation Administration Cumulative.
Environmental Impact Assessment Myriam Raiche November 8, 2007.
The EU Water Framework Directive and Sediments The Water Framework Directive was transposed into law in EU Member States at the end of Nearly two.
AN INTRODUCTION TO STRATEGIC ENVIRONMENTAL ASSESSMENT
Moving towards a more comprehensive planning SEA and indicators Per Christensen Aalborg University Denmark.
Capacity Enhancement for Air Quality Management John E. Hay Senior Advisor UNEP ROAP & IETC.
Identify Problems, Planning Objectives and Constraints
Title slide PIPELINE QRA SEMINAR. PIPELINE RISK ASSESSMENT INTRODUCTION TO GENERAL RISK MANAGEMENT 2.
IPCC Synthesis Report Part I Overview How to address the issue of “dangerous anthropogenic perturbation” to the climate system The relationship between.
LINKAGES AND SYNERGIES OF REGIONAL AND GLOBAL EMISSION CONTROL Workshop of the UN/ECE Task Force on Integrated Assessment Modelling January 27-29, 2003.
FAO/WHO CODEX TRAINING PACKAGE
Vulnerability and Adaptation Assessments Hands-On Training Workshop
INTEGRATED ASSESSMENT AND PLANNING FOR SUSTAINABLE DEVELOPMENT 1 Click to edit Master title style 1 Integrated Assessment and Planning for Sustainable.
What If I Must Go Beyond a Preliminary Assessment? (the example of a USAID EA under Reg. 216) [DATE][SPEAKERS NAMES]
Life Cycle Overview & Resources. Life Cycle Management What is it? Integrated concept for managing goods and services towards more sustainable production.
Environmental Impact Assessment (EIA): Overview
Knowledge on HIA IN CAMBODIA Constructing a Caring and Sharing Community Roles of HIA 4-6 October 2012 Bangkok.
Integrated Assessment and Planning
© 2009 UNDP. All Rights Reserved Worldwide. Proprietary and Confidential. Not For Distribution Without Prior Written Permission. Overview of GEF’s STRATEGIC.
Discussion of Draft CEQ Guidelines for Addressing Climate Change in NEPA Projects Tim Stroope, NEPA Coordinator, GMUG National Forest
Center for International Climate and Environmental Research-Oslo: Research Priorities and Interest in China Lin Gan SINCIERE Member Workshop October 19,
CHAPTER 6 HUMANS IN THE BIOSPHERE
Global Environmental Issues
HUMANS IN THE BIOSPHERE. A Changing Landscape  Growing populations depend on the limited natural resources of earth for survival.  Humans rely on ecological.
IWRM as a Tool for Adaptation to Climate Change
Presented by: The Ohio Department of Transportation 1 Land Use Managing the Environmental & Project Development Process.
What If I Have to Go Beyond an IEE?. EA Training Course Tellus Institute 2 Environmental Assessments (EAs) & Programmatic Environmental Assessments (PEAs)
Final Conference June Maastricht, The Netherlands 1 Case Study: Kłodnica catchment, (Odra river basin) Poland Janusz Krupanek Institut for Ecology.
Wetlands and Poverty Reduction Project Anglophone regional practitioners training course MODULE 3 POLICY SETTING AND ADVOCACY By Teddy Tindamanyire, Isah.
Chapter 6 Humans in the Biosphere
Watershed Assessment and Planning. Review Watershed Hydrology Watershed Hydrology Watershed Characteristics and Processes Watershed Characteristics and.
Humans in the Biosphere. A Changing Landscape * Human activities change the flow of energy in an ecosystem and can reduce the ability of ecosystems to.
UNEP Training Resource ManualTopic 1 Slide 1 Aims and objectives of EIA F modify and improve design F ensure efficient resource use F enhance social aspects.
Investment in Sustainable Natural Resource Management (focus: Agriculture) increases in agricultural productivity have come in part at the expense of deterioration.
1 Improving Statistics for Food Security, Sustainable Agriculture and Rural Development – Action Plan for Africa THE RESEARCH COMPONENT OF THE IMPLEMENTATION.
Kavala Workshop 1-2 June 2006 Legal protection of Transitional Waters [in the Cadses area]: A comparative analysis Dr. Petros Patronos / Dr. Liliana Maslarova.
Secondary & Cumulative Effects Analysis Training Program Maryland State Highway Administration’s Secondary and Cumulative Effects Analysis Guidelines For.
OVERVIEW OF CUMULATIVE EFFECTS ASSESSMENT
VEHICLES FOR SUSTAINABLE DEVELOPMENT. Sustainable Development and Environmental Awareness2 Lesson Learning Goals At the end of this lesson you should.
ENVIRONMENTAL IMPACT ASSESSMENT: Managing Hydropower, Mining and Infrastructure Development Impacts on Natural Capital Iain Watson Senior Environmental.
1 Policy Analysis for RISPO II National Workshop XXXXX 2006.
STRATEGIC ENVIRONMENTAL ASSESSMENT METHODOLOGY AND TECHNIQUES.
INTRODUCTION TO ENVIRONMENTAL IMPACT ASSESSMENT. EIA Procedures and Decision Making 2 Course Learning Objectives At the end of this course you should.
2006 Cumulative Effects Assessment CEA Definition  Potential for residual project-specific effects associated with Meadowbank project in combination.
Sample Codes of Ethics in Adventure Tourism
Lesson 4 ODOT Best Practices. Best Practices Our Challenge: Best Practices for Action-Focused and Resource-Focused analyses are distinct Distinct best.
1 Chapter 1: Introduction to the Environmental Science Introduction to the Environment Mr. Yim Mongtoeun Department of Environmental Science Royal University.
Humans in the Biosphere Chapter 6 Mrs. Yanac. Limited Resources All organisms on Earth must share the planet’s resources and they are LIMITED. Humans.
CUMULATIVE EFFECTS ASSESSMENT METHODOLOGY AND TECHNIQUES.
Environment and Disaster Planning Hari Srinivas, GDRC Rajib Shaw, Kyoto University Contents of the presentation: -What is the problem? -Precautionary Principles.
by Scott J. Callan and Janet M. Thomas
Human Population Growth and Natural Resources Air Quality Water Quality Threats to Biodiversity Conservation
Rob Verheem The Netherlands EIA Commission
UNEP EIA Training Resource ManualTopic 14Slide 1 What is SEA? F systematic, transparent process F instrument for decision-making F addresses environmental.
MEKONG RIVER COMMISSION PROGRAMMES FOR SUSTAINABLE DEVELOPMENT.
Marco Martuzzi World Health Organization Regional Office for Europe Health Impact Assessment as part of SEA.
INTRODUCTION TO ENVIRONMENTAL MODELING. EIA Scientific Tools and Techniques2 Lesson Learning Goals At the end of this lesson you should be able to: 
MRERP Missouri River Ecosystem Restoration Plan and Environmental Impact Statement One River ▪ One Vision A Component of the Missouri River Recovery Program.
TRAP 5 th interregional meeting & Site Visits Limerick & Lough Derg, Ireland 9 th October 2013 CP3 GP6 Regional Planning Guidelines PP3 – Mid-West Regional.
General introduction Florence Agyei-Martey. National Land Use  There is weak linkage at all levels between land use planning and socio- economic development.
EIAScreening6(Gajaseni, 2007)1 II. Scoping. EIAScreening6(Gajaseni, 2007)2 Scoping Definition: is a process of interaction between the interested public,
Strategic Environmental Assessment Patrick White and Nelly Isyagi.
Ecology Human Activities 7/9/2016 SB4d1 Standard  Students will assess the dependence of all organisms on one another and the flow of energy and matter.
Chapter 6 Humans in the Biosphere
CP3 GP6 Regional Planning Guidelines PP3 – Mid-West Regional Authority
5. Impact assessment world café: Cumulative impacts
Strategic Environmental Assessment (SEA)
Presentation transcript:

AN INTRODUCTION TO CUMULATIVE EFFECTS ASSESSMENT

Cumulative Effects Assessment 2 Course Learning Objectives At the end of this course you should be able to:  Describe the elements of cumulative effects assessment (CEA)  Identify the limitations of project-level EIA in addressing potential cumulative impacts  Illustrate with examples the cumulative effects of natural resource development activities in the MRB  Describe how individual projects and activities can cause both local and regional impacts

Cumulative Effects Assessment 3 Course Learning Objectives (Cont’d) At the end of this course you should be able to:  Identify examples of cumulative spatial and temporal impacts  Explain how to assess cumulative and transboundary impacts of resource development activities  Discuss potential barriers to undertaking CEA in MRB riparian countries

Cumulative Effects Assessment 4 Lesson Learning Goals At the end of this lesson you should be able to:  Define CEA and describe its potential application in assessing proposed projects and/or activities  Discuss the potential for cumulative impacts to occur from multiple resource development activities  List types of cumulative impacts  Identify technical and institutional challenges in implementing CEA

Cumulative Effects Assessment 5 The process of systematically identifying and analyzing cumulative environmental change as a result of policies, plans, programs and projects What is Cumulative Effects Assessment? Definition:

Cumulative Effects Assessment 6 to ensure that incremental effects resulting from the combined influences of various actions are properly assessed What is Cumulative Effects Assessment? (Cont’d) Purpose:

Cumulative Effects Assessment 7 “Cumulative EIA is environmental assessment as it should have always been, an EIA done well.” What is Cumulative Effects Assessment? (Cont’d) (Duinker, 1994)

Cumulative Effects Assessment 8 Objectives of EIA  Ensure that potential environmental effects are considered before decisions are made  Promote sustainable development  Prevent adverse environmental effects outside of jurisdictions where proposed projects and developments are to be located  Provide opportunity for public participation in decision-making processes

Cumulative Effects Assessment 9 Limitations of Project-Level EIA in Practice The practice of EIA has generally been limited to evaluating impacts from specific projects and has often excluded the evaluation of cumulative impacts

Cumulative Effects Assessment 10 Limitations of Project-Level EIA in Practice (Cont’d)  Ignores additive effects of repeated developments in the same ecological system  Inadequately addresses precedent-setting developments that stimulate other activities, which may not be desirable  Often ineffective at addressing large-scale and transboundary impacts

Cumulative Effects Assessment 11 What are Cumulative Environmental Impacts? The additive and interactive effects of human activities on an ecosystem over space and time Definition:

Cumulative Effects Assessment 12 What are Cumulative Environmental Impacts? (Cont’d)  Single effects almost never occur in isolation, but occur together with many other influences  Long-term changes may occur not only as a result of a single action but the combined effects or impacts of each successive action on the environment

Cumulative Effects Assessment 13  Individually minor actions that are insignificant on their own can collectively result in significant impacts over a period of time  Cumulative impacts result from the accumulation of human-induced changes across space and over time What are Cumulative Environmental Impacts? (Cont’d)

Example of Cumulative Effects at a Local Scale INDUSTRY FARM RIVER CITY Effluent Discharge Run-off (e.g., pesticides) Sewage

Cumulative Effects Assessment 15 Examples of Cumulative Effects at the Regional Scale Air: combined SO 2 emissions within a regional airshed from three natural gas processing plants Water: combined reductions in flow volumes within a river resulting from irrigation, municipal and industrial water withdrawals Resource use: continual removal of timber from a management area

Cumulative Effects Assessment 16 Cumulative Global Impacts of Concern Global impacts of concern: »Global warming due to increased concentrations of greenhouse gases »Ozone depletion due to increased concentrations of CFCs »Acidification of water bodies due to acid rain »Decline in biodiversity due to alteration and loss of habitat, pollution, overharvesting, etc.

Cumulative Effects Assessment 17 How Do Cumulative Effects Occur? Cumulative impacts arise from spatial and temporal crowding - too much is happening in an area and/or it is happening too frequently

Cumulative Effects Assessment 18 How Do Cumulative Effects Occur? (Cont’d)  The same kind of activity recurs too frequently through time (e.g., harvesting trees or fish above natural regeneration rates)  The same kind of activities recur too densely through space (e.g., urbanization)  Different kinds of activities impose similar consequences on a valued resource (e.g., fishing, loss of habitat, and pollution all combine to result in diminished fish stocks)

Cumulative Effects Assessment 19 Types of Cumulative Impacts  Additive: equal to the sum of individual effects  Interactive: greater than the sum of individual effects »Magnification »Synergistic

Habitat Fragmentation: An Example of Additive Impacts

Cumulative Effects Assessment 21 Biomagnification: An Example of Interactive Impacts A process whereby the concentration of a contaminant in the tissues increases as it passes through one or more trophic levels Water Sediment = contaminant

Cumulative Effects Assessment 22 Contaminant Synergism: An Example of Interactive Effects For example: the toxicity of a mixture of chemicals could be greater than would be expected from simply adding the toxicity of the individual chemicals + =

Cumulative Effects Assessment 23 Repeat Offences:  repeated occurrences of the same small- scale events at the same place (e.g., fishing, salinization of soil from repeated irrigation) Nibbling:  similar small-scale events happening simultaneously (e.g., loss of forest habitat during settlement and establishment of agriculture) Major Cumulative Impact Situations (Duinker, 1994)

Cumulative Effects Assessment 24 Multiple Effects:  several different responses of an ecosystem to one single action (e.g., forest harvesting results in loss of habitat for birds and wildlife, soil erosion, increased sedimentation to rivers) Major Cumulative Impact Situations (Cont’d) (Duinker, 1994)

Cumulative Effects Assessment 25 Multiple Causes:  several agents of change occurring on an ecosystem or VEC (e.g., multiple industrial discharges or decrease in fish population as a result of multiple stresses such as of fishing, hydroelectric development and industrial discharges) Major Cumulative Impact Situations (Cont’d) (Duinker, 1994)

Functional Pathways that Contribute to Cumulative Effects from Multiple Causes Adapted from Peterson et al., 1987 Pathways that lead to Cumulative Effects Persistent Additions From One Process Additive Compounding Effects: Involving 2 or More Processes Interactive: Magnification Interactive: Synergistic Additive

Cumulative Effects Assessment 27 Why do Cumulative Impact Become Difficult Problems? DECREASE IN PREDICTABILITY INCREASE IN SPACE AND TIME Additive Effects Multiplying Effects Discontinuous Effects Long-term System Change

Cumulative Effects Assessment 28  There is increasing evidence that the most devastating environmental effects may not be from the direct effects of a particular action, but from the combination of individual minor effects of multiple actions over time  Consideration of the potential for new projects to exacerbate these problems has not been effectively integrated into project-level EIAs Why is CEA Important?

Cumulative Effects Assessment 29 Advantages of CEA  Provides an estimate of the incremental impact of a proposed project or activity and of the total impact to the environment after addition of the increment  Assesses not just single projects but concurrent or similar projects occurring sequentially in an area

Cumulative Effects Assessment 30  Evaluates environmental impacts of policy, program and plans in addition to projects  Assesses effects over larger areas and can address transboundary concerns  Assesses effects during longer time periods, into the past and future  Evaluates significant effects taking into account cumulative, regional and global effects Advantages of CEA (Cont’d)

Cumulative Effects Assessment 31 Considered best practice in environmental impact assessments Advantages of CEA (Cont’d)

Cumulative Effects Assessment 32 Scales of Analysis for Addressing Cumulative Impacts Project-level CEA: evaluates the interaction from all potential impacts associated with a project and with effects from other projects (i.e., past, present and foreseeable future) Strategic Environmental Assessment (SEA): evaluates potential direct, indirect and cumulative impacts of alternative actions, and decisions made at the policy and planning level; evaluates potential impacts to a region from all actions (i.e., past, present and foreseeable future)

Cumulative Effects Assessment 33 Distinction between Project- Level EIA, Project-Level CEA and SEA  Project-level EIA addresses specific issues and impacts at specific locations  Project-level CEA addresses all issues of the EIA but also incorporates assessment of cumulative effects  SEA is broader in scope and is used to direct human activities (e.g., proactively guide policy and planning development to address cumulative impact concerns)

Comparison of Focus Between EIA and Project- Level CEA EIA Policy and Planning Proposed Project Individual VECs Project-Level CEA Policy and Planning Proposed Project Individual VECs & Total Impact Current Projects Past Projects Future Projects

Comparison of Focus Between Project-Level CEA and SEA Past Projects Policy and Planning Proposed Project Individual VECs & Total Impact Current Projects Future Projects Project-Level CEA Policy and Planning Proposed Projects SEA

Cumulative Effects Assessment 36 Challenges in Undertaking CEA  Numerous scientific and institutional barriers exist to the implementation of CEA »environmental and ecosystem complexity »difficulties in measuring individual effects »lack of attention to defining appropriate spatial and temporal boundaries »lack of sustained interest in monitoring and managing cumulative effects

Cumulative Effects Assessment 37 Lack of Guidelines  Few technical regulations or guidelines have been developed for planning and conducting CEA  In the absence of specific guidelines, it is often easy to not address cumulative impacts at all »in instances where cumulative impacts are addressed, they may be not be considered until quite late in the EIA process

Cumulative Effects Assessment 38 Uncertainty  There will always some degree of uncertainty associated with CEA »scientific expertise and techniques may be inadequate »historical background data may not exist »new or unproven technology may be included in the project proposal

Cumulative Effects Assessment 39 Uncertainty (Cont’d)  Another major source of uncertainty relates to what future projects should be considered in the CEA, and when those projects are scheduled to proceed  Use a weight-of-evidence approach when evaluating which projects to consider within the context of the current proposal »in other words, how strong are the indicators that the other projects will proceed?

Cumulative Effects Assessment 40 CEA Guidelines  The development of effective criteria and guidelines for CEA is one of the best ways to overcome the barriers to CEA  The Canadian Cumulative Effects Assessment Working Group has developed some guidelines »these could be adapted for use in the Lower Mekong Basin

Cumulative Effects Assessment 41 CEA Guidelines 1.The study area is large enough to allow the assessment of VECs that may be affected by the project. This may result in an area that is considerably larger than the project's ‘footprint’. Each VEC may have a different study area.

Cumulative Effects Assessment 42 CEA Guidelines (Cont’d) 2.Other actions that have occurred, exist, or may yet occur which may also affect those same VECs are identified. Future actions that are approved within the study area must be considered if they may affect those VECs and there is enough information about them to assess their effects. Some of these actions may be outside the study area if their influence extends for considerable distances and length of time.

Cumulative Effects Assessment 43 CEA Guidelines (Cont’d) 3.The incremental additive effects of the proposed project on the VECs are assessed. If the nature of the effect's interaction is more complex (e.g., may be synergistic), then assess the effect on that basis, or explain why that is not reasonable or possible. 4.The total effect of the proposed project and other actions on the VECs is assessed.

Cumulative Effects Assessment 44 CEA Guidelines (Cont’d) 5.These total effects are compared to thresholds or policies, if available, and the implications to the VECs are assessed. 6.The analysis of these effects use quantitative techniques, if available, based on best available data. This should be enhanced by qualitative discussion based on best professional judgment.

Cumulative Effects Assessment 45 CEA Guidelines (Cont’d) 7.Mitigation, monitoring and effects management should be recommended (i.e., perhaps as part of an Environmental Protection Plan). These measures may be required at a regional scale (possibly with other stakeholders) to address broader concerns of effects on VECs. 8.The significance of residual effects are clearly stated and defended.

Cumulative Effects Assessment 46 Concluding Thoughts Important points to remember are:  Cumulative impacts are the additive and interactive effects of various projects and activities on an ecosystem over space and time  Limited knowledge and understanding of ecosystems represents a major challenge in predicting and mitigating cumulative impacts  In the absence of specific CEA requirements and guidelines, cumulative impacts are rarely addressed in a comprehensive and timely manner