![]() | Conducting Environmental Impact Assessment in Developing Countries (United Nations University, 1999, 375 p.) |
![]() | ![]() | (introduction...) |
![]() | ![]() | Preface |
![]() | ![]() | Abbreviations |
![]() | ![]() | 1. Introduction |
![]() | ![]() | 1.1 The environmental movement |
![]() | ![]() | 1.2 Tracing the history of environmental impact assessment |
![]() | ![]() | 1.3 Changes in the perception of EIA |
![]() | ![]() | (introduction...) |
![]() | ![]() | 1.3.1 EIA at the project level |
![]() | ![]() | 1.3.2 From project level to regional EIA |
![]() | ![]() | 1.3.3 Policy level strategic EIA |
![]() | ![]() | FURTHER READING |
![]() | ![]() | 2. Introduction to EIA |
![]() | ![]() | 2.1 What is EIA? |
![]() | ![]() | 2.2 Who is involved in the EIA process? |
![]() | ![]() | 2.3 When should the EIA be undertaken? |
![]() | ![]() | 2.4 Effectiveness of EIA |
![]() | ![]() | (introduction...) |
![]() | ![]() | 2.4.1 Legal regulations |
![]() | ![]() | 2.4.2 Rational and open decision-making |
![]() | ![]() | 2.4.3 Project EIA sustained by strategic EIA |
![]() | ![]() | 2.4.4 Room for public participation |
![]() | ![]() | 2.4.5 Independent review and central information |
![]() | ![]() | 2.4.6 Scoping in EIA |
![]() | ![]() | 2.4.7 Quality of the EIA |
![]() | ![]() | 2.5 EIA and other environmental management tools |
![]() | ![]() | 3. EIA process |
![]() | ![]() | 3.1 Introduction |
![]() | ![]() | 3.2 Principles in managing EIA |
![]() | ![]() | (introduction...) |
![]() | ![]() | 3.2.1 Principle 1: Focus on the main issues |
![]() | ![]() | 3.2.2 Principle 2: Involve the appropriate persons and groups |
![]() | ![]() | 3.2.3 Principle 3: Link information to decisions about the project |
![]() | ![]() | 3.2.4 Principle 4: Present clear options for the mitigation of impacts and for sound environmental management |
![]() | ![]() | 3.2.5 Principle 5: Provide information in a form useful to the decision makers |
![]() | ![]() | 3.3 Framework of environmental impacts |
![]() | ![]() | 3.4 EIA process in tiers |
![]() | ![]() | (introduction...) |
![]() | ![]() | 3.4.1 Screening |
![]() | ![]() | (introduction...) |
![]() | ![]() | 3.4.1.1 Illustrations of screening |
![]() | ![]() | 3.4.2 Scoping |
![]() | ![]() | 3.4.3 The initial environmental examination |
![]() | ![]() | 3.4.4 The detailed EIA study |
![]() | ![]() | (introduction...) |
![]() | ![]() | 3.4.4.1 Prediction |
![]() | ![]() | 3.4.4.2 Assessment |
![]() | ![]() | 3.4.4.3 Mitigation |
![]() | ![]() | 3.4.4.4 Evaluation |
![]() | ![]() | 3.5 Resources needed for an EIA |
![]() | ![]() | 3.6 Some illustrations of EIA processes in various countries |
![]() | ![]() | (introduction...) |
![]() | ![]() | 3.6.1 EIA system in Indonesia |
![]() | ![]() | (introduction...) |
![]() | ![]() | 3.6.1.1 Responsibility for AMDAL |
![]() | ![]() | 3.6.1.2 Screening: determining which projects require AMDAL |
![]() | ![]() | 3.6.1.3 AMDAL procedures |
![]() | ![]() | 3.6.1.4 Permits and licenses |
![]() | ![]() | 3.6.1.5 Public participation in AMDAL |
![]() | ![]() | 3.6.2 EIA procedure and requirements in Malaysia |
![]() | ![]() | (introduction...) |
![]() | ![]() | 3.6.2.1 Integrated project-planning concept |
![]() | ![]() | 3.6.2.2 How is EIA processed and approved? |
![]() | ![]() | 3.6.3 EIA in Canada |
![]() | ![]() | (introduction...) |
![]() | ![]() | 3.6.3.1 The process |
![]() | ![]() | FURTHER READING |
![]() | ![]() | 4. EIA methods |
![]() | ![]() | 4.1 Introduction |
![]() | ![]() | 4.2 Checklists |
![]() | ![]() | 4.2.1 Descriptive checklists |
![]() | ![]() | (introduction...) |
![]() | ![]() | 4.2.2 Weighted-scale checklists |
![]() | ![]() | 4.2.3 Advantages of the checklist method |
![]() | ![]() | 4.2.4 Limitations of the checklist method |
![]() | ![]() | 4.3 Matrix |
![]() | ![]() | (introduction...) |
![]() | ![]() | 4.3.1 Descriptive matrix |
![]() | ![]() | 4.3.2 Symbolized matrix |
![]() | ![]() | 4.3.3 Numeric and scaled matrices |
![]() | ![]() | 4.3.3.1 Simple numeric matrix |
![]() | ![]() | 4.3.3.2 Scaled matrices |
![]() | ![]() | 4.3.4 The component interaction matrix |
![]() | ![]() | 4.3.5 Advantages of the matrix approach |
![]() | ![]() | 4.3.6 Limitations of the matrix approach |
![]() | ![]() | 4.4 Networks |
![]() | ![]() | (introduction...) |
![]() | ![]() | 4.4.1 Advantages of the network method |
![]() | ![]() | 4.4.2 Limitations of the network method |
![]() | ![]() | 4.5 Overlays |
![]() | ![]() | FURTHER READING |
![]() | ![]() | 5. EIA tools |
![]() | ![]() | 5.1 Impact prediction |
![]() | ![]() | (introduction...) |
![]() | ![]() | 5.1.1 Application of methods to different levels of prediction |
![]() | ![]() | 5.1.2 Informal modelling |
![]() | ![]() | (introduction...) |
![]() | ![]() | 5.1.2.1 Approaches to informal modelling |
![]() | ![]() | 5.1.3 Physical models |
![]() | ![]() | 5.1.4 Mathematical models |
![]() | ![]() | 5.1.5 Modelling procedure |
![]() | ![]() | 5.1.6 Sensitivity analysis |
![]() | ![]() | 5.1.7 Probabilistic modelling |
![]() | ![]() | 5.1.8 Points to be considered when selecting a prediction model |
![]() | ![]() | 5.1.9 Difficulties in prediction |
![]() | ![]() | 5.1.10 Auditing of EIAs |
![]() | ![]() | (introduction...) |
![]() | ![]() | 5.1.10.1 Auditing prediction in EIAs |
![]() | ![]() | 5.1.10.2 Problems in conducting predictive techniques audit |
![]() | ![]() | 5.1.11 Precision in prediction and decision resolution |
![]() | ![]() | 5.2 Geographical information system |
![]() | ![]() | (introduction...) |
![]() | ![]() | 5.2.1 Data overlay and analysis |
![]() | ![]() | 5.2.2 Site impact prediction |
![]() | ![]() | 5.2.3 Wider area impact prediction |
![]() | ![]() | 5.2.4 Corridor analysis |
![]() | ![]() | 5.2.5 Cumulative effects assessment and EA audits |
![]() | ![]() | 5.2.6 Trend analysis |
![]() | ![]() | 5.2.7 Predicting impacts in a real time environment |
![]() | ![]() | 5.2.8 Continuous updating |
![]() | ![]() | 5.2.9 Multi attribute tradeoff system (MATS) |
![]() | ![]() | 5.2.10 Habitat analysis |
![]() | ![]() | 5.2.11 Aesthetic analysis |
![]() | ![]() | 5.2.12 Public consultation |
![]() | ![]() | 5.2.13 Advantages of the GIS method |
![]() | ![]() | 5.2.14 Limitations of the GIS method |
![]() | ![]() | 5.3 Expert systems for EIA |
![]() | ![]() | (introduction...) |
![]() | ![]() | 5.3.1 Artificial intelligence and expert systems |
![]() | ![]() | 5.3.2 Basic concepts behind expert systems |
![]() | ![]() | FURTHER READING |
![]() | ![]() | 6. Environmental management measures and monitoring |
![]() | ![]() | 6.1 Introduction |
![]() | ![]() | 6.2 Environmental management plan (EMP) |
![]() | ![]() | (introduction...) |
![]() | ![]() | 6.2.1 Issues and mitigation measures |
![]() | ![]() | (introduction...) |
![]() | ![]() | 6.2.1.1 Project siting |
![]() | ![]() | 6.2.1.2 Plant construction and operation |
![]() | ![]() | 6.2.2 Illustrations of guidelines for mitigation measures for specific projects |
![]() | ![]() | (introduction...) |
![]() | ![]() | 6.2.2.1 Fertilizer industry |
![]() | ![]() | 6.2.2.2 Oil and gas pipelines |
![]() | ![]() | 6.2.2.3 Water resource projects |
![]() | ![]() | 6.2.2.4 Infrastructure projects |
![]() | ![]() | 6.2.3 Development of a green belt as a mitigation measure |
![]() | ![]() | 6.3 Post-project monitoring, post-audit, and evaluation |
![]() | ![]() | FURTHER READING |
![]() | ![]() | 7. EIA communication |
![]() | ![]() | 7.1 Introduction |
![]() | ![]() | 7.2 What is expected from the user of EIA findings? |
![]() | ![]() | 7.3 Communication to the public |
![]() | ![]() | (introduction...) |
![]() | ![]() | 7.3.1 Factors that may result in effective public participation |
![]() | ![]() | (introduction...) |
![]() | ![]() | 7.3.1.1 Preplanning |
![]() | ![]() | 7.3.1.2 Policy of the executing agency |
![]() | ![]() | 7.3.1.3 Resources |
![]() | ![]() | 7.3.1.4 Target groups |
![]() | ![]() | 7.3.1.5 Effective communication |
![]() | ![]() | 7.3.1.6 Techniques |
![]() | ![]() | 7.3.1.7 Responsiveness |
![]() | ![]() | 7.3.2 Overview of the roles of the public |
![]() | ![]() | 7.3.3 Public participation techniques |
![]() | ![]() | (introduction...) |
![]() | ![]() | 7.3.3.1 Media techniques |
![]() | ![]() | 7.3.3.2 Research techniques |
![]() | ![]() | 7.3.3.3 Political techniques |
![]() | ![]() | 7.3.3.4 Structured group techniques |
![]() | ![]() | 7.3.3.5 Large group meetings |
![]() | ![]() | 7.3.3.6 Bureaucratic decentralization |
![]() | ![]() | 7.3.3.7 Interveners |
![]() | ![]() | 7.3.4 Implementing public participation |
![]() | ![]() | FURTHER READING |
![]() | ![]() | 8. Writing and reviewing an EIA report |
![]() | ![]() | 8.1 Writing an EIA report |
![]() | ![]() | (introduction...) |
![]() | ![]() | 8.1.1 Guidelines for preparing EIA reports |
![]() | ![]() | 8.1.2 Comparison of guidelines of suggested/required components of an EIA report |
![]() | ![]() | 8.2 Review of an EIA report |
![]() | ![]() | (introduction...) |
![]() | ![]() | 8.2.1 Purpose of the review |
![]() | ![]() | 8.2.2 Information and expertise needed for review |
![]() | ![]() | 8.2.3 Strategy of the review |
![]() | ![]() | 8.2.4 Approach |
![]() | ![]() | (introduction...) |
![]() | ![]() | 8.2.4.1 Independent analysis |
![]() | ![]() | 8.2.4.2 Predetermined evaluation criteria |
![]() | ![]() | 8.2.4.3 Ad hoc review |
![]() | ![]() | 8.2.5 Specific document review criteria |
![]() | ![]() | 8.3 Preparing terms of reference for consultants or contractors |
![]() | ![]() | (introduction...) |
![]() | ![]() | 8.3.1 Checking out the consulting organization |
![]() | ![]() | 8.3.2 Strategy for formulating TOR |
![]() | ![]() | FURTHER READING |
![]() | ![]() | 9. Emerging developments in EIA |
![]() | ![]() | 9.1 Introduction |
![]() | ![]() | 9.2 Cumulative effects assessment |
![]() | ![]() | (introduction...) |
![]() | ![]() | 9.2.1 Concepts and principles relevant to CEA |
![]() | ![]() | (introduction...) |
![]() | ![]() | 9.2.1.1 Model of causality |
![]() | ![]() | 9.2.1.2 Input-process-output model |
![]() | ![]() | 9.2.1.3 Temporal and spatial accumulation |
![]() | ![]() | 9.2.1.4 Control factors |
![]() | ![]() | 9.2.2 Conceptual framework |
![]() | ![]() | (introduction...) |
![]() | ![]() | 9.2.2.1 Sources of cumulative environmental change |
![]() | ![]() | 9.2.2.2 Pathways of cumulative environmental change |
![]() | ![]() | 9.2.2.3 Cumulative effects |
![]() | ![]() | 9.2.3 Conclusion |
![]() | ![]() | 9.3 Sectoral environmental assessment |
![]() | ![]() | (introduction...) |
![]() | ![]() | 9.3.1 Need for SEA |
![]() | ![]() | 9.3.2 Differences between project level EIA and SEA |
![]() | ![]() | 9.3.3 Methodologies for SEA |
![]() | ![]() | 9.3.4 Status of SEA |
![]() | ![]() | 9.3.5 Effectiveness of SEA |
![]() | ![]() | 9.4 Environmental risk assessments |
![]() | ![]() | 9.4.1 What is environmental risk assessment? |
![]() | ![]() | 9.4.2 Terminology associated with ERA |
![]() | ![]() | (introduction...) |
![]() | ![]() | 9.4.2.1 Hazards and uncertainties |
![]() | ![]() | 9.4.3 ERA and the project cycle |
![]() | ![]() | 9.4.4 ERA builds upon EIA |
![]() | ![]() | 9.4.5 Basic approach to ERA |
![]() | ![]() | 9.4.6 Characterization of risk |
![]() | ![]() | 9.4.7 Risk comparison |
![]() | ![]() | 9.4.8 Quantitative risk assessments |
![]() | ![]() | 9.4.9 Risk communication |
![]() | ![]() | 9.4.10 Risk management |
![]() | ![]() | 9.4.11 Guidelines for disaster management planning |
![]() | ![]() | (introduction...) |
![]() | ![]() | 9.4.11.1 Specification |
![]() | ![]() | 9.4.11.2 Plot plan |
![]() | ![]() | 9.4.11.3 Hazardous area classification |
![]() | ![]() | 9.4.11.4 P & I diagrams |
![]() | ![]() | 9.4.11.5 Storage of inflammable liquids |
![]() | ![]() | 9.4.11.6 Risk assessment |
![]() | ![]() | 9.5 Environmental health impact assessment |
![]() | ![]() | (introduction...) |
![]() | ![]() | 9.5.1 Need for EHIA |
![]() | ![]() | 9.5.2 Potential methodologies and approaches for addressing health impacts |
![]() | ![]() | (introduction...) |
![]() | ![]() | 9.5.2.1 Adapt EIA study activities |
![]() | ![]() | 9.5.2.2 Integrate health impacts into EIA |
![]() | ![]() | 9.5.2.3 Use a targeted approach |
![]() | ![]() | 9.5.2.4 Probabilistic risk assessment |
![]() | ![]() | 9.5.3 Proposed methodology |
![]() | ![]() | (introduction...) |
![]() | ![]() | 9.5.3.1 Determining the need for health impact assessment |
![]() | ![]() | 9.5.3.2 Identify health impacts |
![]() | ![]() | 9.5.3.3 Prediction of health impacts |
![]() | ![]() | 9.5.3.4 Interpreting health impacts |
![]() | ![]() | 9.5.3.5 Mitigation, monitoring, and reporting |
![]() | ![]() | 9.6 Social impact assessment |
![]() | ![]() | 9.6.1 What is SIA? Why SIA? |
![]() | ![]() | 9.6.2 Identifying social impact assessment variables |
![]() | ![]() | 9.6.3 Combining social impact assessment variables, project/policy stage, and setting |
![]() | ![]() | 9.6.4 Steps in the social impact assessment process |
![]() | ![]() | (introduction...) |
![]() | ![]() | 9.6.4.1 Public involvement |
![]() | ![]() | 9.6.4.2 Identification of alternatives |
![]() | ![]() | 9.6.4.3 Baseline conditions |
![]() | ![]() | 9.6.4.4 Scoping |
![]() | ![]() | 9.6.4.5 Projection of estimated effects |
![]() | ![]() | 9.6.4.6 Predicting response to impacts |
![]() | ![]() | 9.6.4.7 Indirect and cumulative impacts |
![]() | ![]() | 9.6.4.8 Change in alternatives |
![]() | ![]() | 9.6.4.9 Mitigation |
![]() | ![]() | 9.6.4.10 Monitoring |
![]() | ![]() | 9.6.5 Principles for SIA |
![]() | ![]() | 9.6.6 TOR for consultants |
![]() | ![]() | FURTHER READING |
![]() | ![]() | Annex 9.1: Case study for risk assessments |
![]() | ![]() | 10. Case studies to illustrate environmental impact assessment studies |
![]() | ![]() | Case study 10.1 Tongonan Geothermal Power Plant, Leyte, Philippines |
![]() | ![]() | Case study 10.2 Accelerated Mahaweli Development Programme |
![]() | ![]() | Case study 10.3 Tin Smelter Project in Thailand |
![]() | ![]() | Case study 10.4 Thai National Fertilizer Corporation Project |
![]() | ![]() | Case study 10.5 Map Ta Phut Port Project |
![]() | ![]() | Case study 10.6 EIA at Work: A Hydroelectric Project in Indonesia |
![]() | ![]() | Case study 10.7 The Greater Cairo Wastewater Project |
Monitoring is required to evaluate the success or failure (and consequent benefits or losses) of environmental management measures and subsequently to reorient the management plan. It is essential that a good detailed monitoring programme be designed for appropriate projects (this design should be prepared as part of the EIA study and should be presented as a major component of the report including the detailed monitoring workplan, reporting procedure, and manpower and costs budgets) and that regular monitoring reports be submitted to environmental agencies. When these procedural needs are fulfilled, the EIA planning tool is put to use in a much more effective manner, and benefit analysis will be possible, which will determine how successful the EIA process is in preventing or minimizing environmental degradation.
The EIA procedures should include a formal requirement to review completed projects and judge the predictions and recommendations made against actual experience. The purposes of such an audit are to determine whether consequences were accurately predicted, to identify additional significant effects warranting corrective action, and to use the results to refine the impact predictions for future projects of the same type and magnitude.
Monitoring is essential for continuing EIA inputs to management (i.e., mid-course corrections, compliance with mitigation actions, and improvement of predictions). We have seen that predictive accuracy is limited because of the scarcity of information on impacts and natural variations in the environment. All development projects should be managed with the expectation of surprising outcomes and the necessity to adapt and change implementation actions if the goals are to be met. Monitoring provides an early warning that adverse impacts (predicted or not) are occurring.
Table 6.7 Definitions of monitoring assessments procedures
Operations |
Definition |
Monitoring |
Long-term, standardized measurement, observation, evaluation, and
reporting of part of the environment in order to define status and
trends |
Survey |
A finite duration, intensive programme to measure, evaluate, and
report the quality of part of the environment for a specific
purpose |
Surveillance |
Continuous, specific measurement, observation, and reporting for
the purpose of environmental management and operational
activities |
Measures recommended to mitigate the impacts of development must be actually installed, operated, and maintained. Even so, their efficacy is often uncertain; thus, monitoring is necessary to see how well they work out and how cost-effective they are. As in the case of post-audit, compliance monitoring should be independent of the project operator, or at least the data should be verified by an independent group.
The overall evaluation of EIA in a particular government should be undertaken from time to time. All participants in the process should contribute constructive criticism and judgement as to how well EIA has helped achieve sustainable development.
The owners of the projects will be obliged to carry out the monitoring or surveillance programme, continuously or at defined intervals, and to report results to the regulatory body. If adverse effects beyond those anticipated in the original environmental impact assessments become apparent, remedial actions would have to be taken. In an extreme case, if suitable remedies cannot be found, closure of the project might be required.
The various procedures that may be adopted during monitoring, and the distinction between them, are shown in Table 6.7.
Monitoring may involve sampling of air, water, and soil, and the data collection programme should be planned to obtain the greatest value from the data, which is often expensive to collect and process. Care should be taken to classify and store data for easy retrieval, so that it can be useful as baseline or reference data for other assessments.
In the few retrospective studies made, the findings have been disconcerting. Forecasts are admittedly difficult, but they are often so imprecise and vague that their accuracy cannot really be ascertained. Many impacts are presented as unquantified assertions without any indication of their likelihood or significance. Not surprisingly, physiographic information is usually more complete and precise than biological impact prediction. Social considerations often occupy disproportionate space (in terms of what is actually known) in an EIA, but that is a reflection of the essential political use of these documents.
The post-audit can begin at once with existing EIAs on completed projects. It is a valuable training device and also helps to find empirical evidence for cause-effect relationships that will be useful in ongoing and future EIAs. Post-audit may be difficult in that the performers of past EIAs are being second guessed. Therefore, it should be carried out by a group independent of the environmental agencies, perhaps a panel drawn from the academic community.
The post-implementation monitoring of a project may involve audits which are somewhat different from the industrial audit. Three types of audit relevant to an EIA on a motorway project are listed here as an example:
• implementation audits, for determining whether the recommendations or requirements in an EIA were implemented;• project impact audits, which determine the actual impacts of a project, independent of the predictions made, and
• predictive techniques audits, assessing the predictions made in the EIA report, and the methods of prediction used, by comparing actual outcome with the forecast ones (this would aid future studies).