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Some features of this site may not work without it. It is a tool for trainers who have some background experience and understanding of EIA. It is designed t assists them in preparing and delivering training coursed that provide an understanding of, and basic capacity in, the application of EIA. The Manual is intended for use and adaptation by persons who are engaged in EIA training. IAIA cooperated in the development of this manual, and with the support of UNEP, is now able to make the manual available on the IAIA website. Dr. Partidario's course on SEA has been one of the best-attended training sessions at IAIA's annual meetings for many years, and gets high ratings from attendees for its presentation of SEA current practices, future demands and capacity building needs. The manual, funded by the European Union, is intended for specific application in Albania, Bosnia and Herzegovina, Croatia, FYR Macedonia, and Serbia and Montenegro including Kosovo). It offers an overview of EIA development in South Eastern Europe, provides a set of training materials for specific countries, and includes a wide collection of relevant documents that can be used in EIA reforms in the region. The manual has been translated and pilot tested in 5 countries. The manual highlights the main requirements of the Protocol on SEA, outlines the key issues for applying the Protocol in practice and provides materials for training and capacity-development programmes supporting application of the Protocol (including a printable manual in English and Russian, slide sets, and links to case studies, other guidance materials and numerous other resources).
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The manual is expected to be used by: (a) those who want to learn about the Protocol and the theory of its application, including government and other officials working on the application of the Protocol, practitioners carrying out SEAs and stakeholders wishing to participate in the SEA process; and (b) those who want to advise and train others on the Protocol's requirements and the application of SEA. The elements of the manual that focus on the application of SEA in practice may also be of use to those applying the European Union's SEA Directive. Explaining the EIA process and legal procedures in a clear and straightforward way, the authors employ their extensive practical experience to cover each of the steps and associated studies needed to undertake an EIA and to produce a successful Environmental Statement. Following the success of the first edition, this second edition is fully updated in line with the Planning Bill enacted in November 2008 and expanded to include a new chapter on Strategic Environmental Assessment (SEA). By using our services, you agree to our use of cookies. Register now We will send you instructions to reset your password. Explaining the EIA process and legal procedures in a clear and straightforward way, the authors employ their extensive practical experience to cover each of the steps and associated studies needed to undertake an EIA and to produce a successful environmental statement. Environmental Impact Assessment Handbook is fully updated in line with EU legislation for ensuring protection of the environment from new development, including the 2014 EU directive transposed into UK law in 2017, which heralds a step-change in scope and approach. Written by practitioners for practitioners, covering procedures, environmental issues and other associated assessments, Environmental Impact Assessment Handbook Students and community groups will also find this a valuable text. Book Reviews This book affirmatively presents as a handbook indeed.
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Written by practitioners, it examines EIA from a practical but also highly educational point of view. It adopts a step-by-step approach to explaining the EIA procedure for practitioners at varied stages of their professional experience. Graduates and students will find the text a useful companion in helping them get a full grasp of the EIA process and more experienced professionals will find the book a useful resource for their professional development especially as a result of updates in regulations and the example case studies. David Oloke, Principal Consultant, Progressive Concept Consultancy Ltd This practical guide is a must for anyone actively involved, or about to become involved, in environmental impact assessments. It is broken down into stages of the assessment process, enabling readers to dip in and out whenever they need advice and support. Each chapter works through the process methodically, identifying the relevant parts of the legislation, providing advice from the authors and presenting case studies. Jo Griffiths, Network Rail, UK This book is the third edition of the practical handbook for Environmental Impact Assessments. It does a great deal to demystify the process and explain in clear language what is needed, when and why. This is very helpful and an excellent manual. (.) This is just the book that can be trusted in clear language to tell us what is required, so that we know and can operate in an informed way. The handbook achieves what it set out to do. It is a step by step logical process of delivering an Environmental Impact Assessment through the various stages. The most important element of the book from my perspective is the thought given to the integration of these processes in the project. The handbook clearly details what is needed at each stage in the project lifecycle.
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An excellent book for planners, developer and communities, as the title suggests, but I would also highly recommend for other construction industry professionals who work in projects that may require EIA, to ensure that they understand the implications, and plan sufficient resources to ensure project success. Veronica Flint Williams, Environment Agency. Would you like to change to the United States site? This is a dummy description.This is a dummy description.This is a dummy description.This is a dummy description.International debate focuses on its enhancement to meet the challenges of sustainable development, as well as facilitating scientifically robust, integrated and participative decision-making. This handbook hopes to contribute an international, multidisciplinary, ready-reference source to this debate. This first volume addresses EIA principles, process and methods. Part 1 maps the EIA process and its impact on decision. It positions EIA in the context of sustainable development and relative to other decision tools, including economic valuation. It also positions strategic environmental assessment (SEA) in a similar way. Part 2 addresses the elements of the EIA process and significant impact assessment topics--air, water, ecological, social, risk, landscape and visual--not only in terms of good practice but also methodological evolution. This volume concludes by addressing cumulative impact assessment and SEA methods. Volume 2 provides a unique consideration for EIA implementation and practice in Europe, Africa, the Far East, South America and North America. It uses a number of project types to provide 'how to do' guidance and addresses practice in policy and plan assessment. This volume should be read by legislators, decision-makers, economists, developers, industrial managers and consultants involved in this significant field. She graduated from the University of Exeter and Loughborough University. Part I: EIA As a Decision Tool. Introduction.
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EIA and Sustainable Development. EIA Versus other Environmental Management Tools. Strategic Environmental Assessment - Principles and Potential. Criteria and Standards for Assessing Significant Impact. EIA, CBA and the Valuation of Environmental Impacts. EIA Impact on Decisions. Public Participation and EIA. EIA and Information Technologies. Part II: EIA Process and Methods. Screening, Scoping and Site-Selection. EIA Monitoring and Auditing. Air Quality Assessment. Water Impact Assessment. Social Impact Assessment. Ecological Assessment. Landscape and Visual Impact Assessment. Risk Assessment. Cumulative Effects Assessment. Methods of Strategic Environmental Assessment. Volume 2: EIA in Practice: Impact and Limitations. Part I: Quality and Effectiveness. Introduction. Comparative Evaluation of EIA Systems. Capacity Building. Quality and Quality Control in EIA. Part II: EIA At the International Level. The Convention of Environmental Impact Assessment in a Transboundary Context. EIA and Multi-Lateral Financial Institutions. Part III: International Experience. EIA in Central and Eastern Europe. EIA in East Asia; EIA in Africa. EIA in South and Central America. EIA in North America. EIA in the European Union. Part IV: Sectoral Experience. Policy Environmental Assessment. EIA of Land-Use Plans: Experience under the National Environmental Policy Act and the California Environmental Quality Act. EIA and Waste Management. EIA of Road and Rail Infrastructure. EIA for Energy Projects. EIA for Mining Projects. EIA for Water Projects.
The steps required are: Bioindicators should be selected that canThe sequential process of increased complexity ofFor example,For example, protectionFor example, a project mayGiven appropriate environmental information, alternative coursesOften this is not done in a sufficiently integrated way, and the EA is seen as an external,This has resulted in EA being viewed as a negative, restrictive practise,The project will have specific objectives and certainThese objectivesIf they did, thenIf not, then the first step is to gatherThe term scoping arises from the USA National. Environmental Policy Act which includes a regulation “there shall be an early and open processScoping is not always accepted, and, depending on theScreening has tended to be a meeting between the planners of theIn this it differs fromThis is not necessarily true,The problem withIssues raised in a broader context can then be taken to theAt this point it is helpful to use aThese use of checklists is discussed inFor instance, the World Bank uses a system ofOnce the decision hasThe checklist ofThe sample checklists provided in Appendix 1, for example, are specific to the type ofWhen assessing the impacts,Effects of theIf a forestry project causesOr if deforestationWhilst remote sensing and aerialThe checklist can beWhilst these twoThere is a danger that these linkages can beIn situations of minimal environmental risk, these actions mayWhere instead severe environmental impacts areCertain areas may need to be consideredSome care should be taken to avoidThus, even if a detailed. EA is not needed, the environmental review process does not terminate at this stage. IfMore detailedA detailed EA will consist of much more thanRather it will contain a substantialSocial impacts, for example, are liable to be substantial (see Chapter 5 for a brief overview ofNeither does it mean that no management is required.
When a forest isWildlife populations can increase in the forest, causing damage to cropsMoreover, authorities doLanka, are considered in Appendix 2 in terms of the economic benefits they have created. The negative impactsThe next question is how current utilisation can be changed to achieveIf declaration of a protected forest in order toThis will result in increasedEnvironmental benefits from protection may be remote fromThis makes levels of compensation difficult to assess. AnotherThis must be borne in mind whenThe aim of most natural forest management is to achieve a double dividend; that is, the forestsThus, the forestsIn order to arrive at aThere are two main reasons for the apparent lackHowever, thisWith increasing populationsChanges over time in both natural and harvested populationsThe emphasis for EA here is on management actions whichThis may involve destructive logging but noIn brief, these include direct impacts on soils,More subtle alteration of vegetation and wildlifeIndirect effects of logging alsoDownstream or offsite effects should be noted to ensure that these are detected early on andMitigation is liable to be important whereOfficial recognition is not enough. If forestShelterwood Systems ). Investment in plantations and afforestation is based on a number of positive impacts (World BankWhile this is obviously true of the overstory trees, some researchers haveParrotta and Brown, 1993). Thus, when designing plantations, natural successional processesSome species improve soil fertility, but othersAn often-cited example of where this was a concern is theOne of the case studiesPlantations are also often susceptible to fire and attack by pests, althoughImpacts associated with wood supply areAs a result, the mill shouldInevitably, as the plant ages, so the pollution abatement measures, equipment and storage facilitiesEffective management decision processes need to beIn particular, an.
EA should consider whether new forest policies address the following: In this case, mitigationOften thereIt is much more effective and cheaper to include mitigation orTo put it another way: crisis management is expensive, embarrassingMitigation and alternatives are most effectively formulatedThere are structuredThe checklists provided in Appendix 1 contain usefulMonitoring should ensure that (World Bank 1991): It is conceivableThe next chapter provides. EIA applies to projects with potential significant adverse impacts on the environment, and informs the development consent process.EIAs are normally prepared under the requirements of national EIA systems, but can also be required by the EU based on its own standards. Meaningful opportunities must be given for all stakeholders and the public in general, to engage throughout the EIA process, in consistency with the obligations under the Aarhus Convention. It also includes the description of the “no project” scenario, based on assumptions regarding future changes. Another important step is the identification and evaluation of the potential significant environmental impacts. The impacts are the differences between the situation with, and the situation without the project. The identification and assessments of impacts are necessary for all alternatives under study, in order to compare them and provide recommendations on the selection of the most environmentally sound alternative. It may be decided to undertake a more detailed assessment of a preferred alternative.See details of service Here are the instructions how to enable JavaScript in your web browser. The 13-digit and 10-digit formats both work. Please try again.Please try again.Please try again. Used: Very GoodClean, undamaged book with no damage to pages and minimal wear to the cover. Spine still tight, in very good condition. Remember if you are not happy, you are covered by our 100 money back guarantee.
International debate focuses on its enhancement to meet the challenges of sustainable development and demands for scientifically robust integrated and participative decision-making. This handbook hopes to improve practice by contributing an international, multidisciplinary, ready-reference source to this debate. Volume I addresses EIA principles, process and methods. Part 1 maps the EIA process and its impact on decision, and positions EIA in the context of sustainable development as well as the other decision tools, including economic valuation. Part 2 addresses the elements of the EIA process and significant impact assessment topics (air, water, ecological, social, risk, landscape and visual), not only in terms of good practice but also methodological evolution. The volume concludes by addressing cumulative impact assessment and SEA methods. This book should be read by legislators, decision-makers, economists, developers, industrial managers and consultants involved in this significant field. Then you can start reading Kindle books on your smartphone, tablet, or computer - no Kindle device required. Register a free business account International debate focuses on its enhancement to meet the challenges of sustainable development, not least demands for scientifically robust integrated and participative decision-making. This Handbook hopes to improve practice by contributing an international, multidisciplinary, ready-reference source to this debate. Part 2 addresses the elements of the EIA process and significant impact assessment topics - air, water, ecological, social, risk, landscape and visual - not only in terms of good practice but also methodological evolution. Volume 2 provides a unique consideration for EIA implementation and practice - in Europe, Africa, the Far East, South America and North America. It uses a number of project types to provide 'how-to-do' guidance and addresses practice in policy and plan assessment.
This book should be ready by legislators, decision makers, economists, developers, industrial managers and consultants involved in this significant field. International debate focuses on its enhancement to meet the challenges of sustainable development, not least demands for scientifically robust integrated and participative decision-making. This book should be ready by legislators, decision makers, economists, developers, industrial managers and consultants involved in this significant field. She graduated from the University of Exeter and Loughborough University.To calculate the overall star rating and percentage breakdown by star, we don’t use a simple average. Instead, our system considers things like how recent a review is and if the reviewer bought the item on Amazon. It also analyzes reviews to verify trustworthiness. As generally understood, SEA is a systematic and anticipatory process, undertaken to analyze the environmental effects of proposed plans, programmes and other strategic actions and to integrate the findings into decision-making. But it also offers In addition, Time efficiency (and as a consequence cost effectiveness) is expected to be improved by better and more consistent decision-making at the plan or programme level, leading to fewer appeals and less discussion at the operational or EIA level. Ultimately, SEA supports project-level decisions as these can be based on previously optimized plans and programmes. The shared use of information produced at different stages of the planning hierarchy may also increase the efficiency of decision-making. It helps in A sound application Properly undertaken It may mobilize public support A more recent study Nonetheless, This will facilitate This might In this context, This approach, The UK approach has As such, it might be followed These are broadly outlined In the present context, Strong arguments There are also various SEA practice at the policy This material and particularly.
The document assists project designers, consultants, regulators and decision makers to anticipate and address all relevant environmental, socioeconomic and public health concerns that may arise when undertaking a desalination project for obtaining maximum beneficial use of the desalinated water in terms of quality, safety and environmental protection. This paper gives a short account of the guidance development process and summarizes the main results and recommendations. The UNEP document is divided into three parts. In part A, an introduction to the concept, methodology and practice of environmental impact assessment (EIA) is given and a 10-step EIA approach is proposed. Part B outlines a possible modular structure of an EIA report and gives an overview on a wide range of thematic issues that may be relevant to desalination projects. Part C discusses the potential impacts of desalination plants on the environment, based on a comprehensive literature review, and evaluates the identified impacts in terms of significance and relevance for EIA studies. Keywords: Desalination, Environment, Socioeconomic, Health, Impact assessment, EIA, UNEP, WHO To learn about our use of cookies and how you can manage your cookie settings, please see our Cookie Policy. By closing this message, you are consenting to our use of cookies. Furthermore, EIA enhances public participation and engages stakeholders to inform decision makers of different views. Additionally, EIA, in conjunction with monitoring Introduction tools and recourse mechanisms, allows the gathering The main focus of this Guidance Note is the use of of information on environmental quality and provides EIA as a policy tool available to policy makers for a venue for expression and discussion of diverging effective pollution management.1 opinions.
This Guidance Note does not discuss the pollution management environmental standards through by EIA facilitates its identifying link to technical aspects of preparing an environmental if the assessment, since numerous resources and good practices are available on preparing an EIA. Instead, ? This guidance note was prepared by Helena Naber (Environmental Economist, ENV), with significant contribution from Ernesto Sanchez-Triana (Lead Environmental Specialist, SASDI) and Santiago Enriquez (Consultant, SASDI), and contribution from Francisco Giner de Los Rios (Consultant). Peer reviewers included Harvey Himberg (Consultant, OCPQC) and Hocine Chalal (Regional Safeguards Adviser, MNACS). Editorial assistance was provided by Stan Wanat (Consultant), Juliette Guantai (Program Assistant) and James Cantrell (Communication Analyst). The task team leaders for this product are Kulsum Ahmed (Lead Environment Specialist, ENV) and Helena Naber (Environmental Economist, ENV). This Guidance Note however does not address the use of EA by the World Bank but rather discusses EA as a tool that may be used by government stakeholders for effective pollution management. For guidance on the World Bank’s environmental assessment policy, please refer to Safeguard Policies on the World Bank site: and to IFC performance standards: ards this Note focuses on the broader use of EIA as a policy instrument within the range of policy instruments discussed in this toolkit, and which are available to different stakeholders for pollution management. Public participation and disclosure are stakeholders into the decision-making of authorities.
The environmental assessment process had an environmental management tool that helps control two major purposes: ensure that decision makers are the environmental impacts of a broad range of making informed choices regarding impacts on the projects, such as in Brazil where authorities often environment and open the process to citizen establish design and operational conditions through involvement (CEQ 2007). Over the past 40 years, EIA the EIA process (World Bank 2008), or Guatemala entered the fabric of environmental governance in (World Bank 2006c) and Nepal (World Bank 2007b), over 100 countries worldwide (Glasson and others where EIA became the main policy instrument to 2005).He further to identify, avoid, and mitigate the potential negative notes that most developing countries start with a form environmental impacts associated with Bank lending of EIA that most closely matches the technical model operations (World Bank 1999). Even though most EIA characterized by a focus on the project level, with systems follow the steps of the generic EIA, there are weak public participation and reliance on quantitative substantive and procedural emphasis differences: measurement rather than qualitative perceptions. Nature of EIA. A country?s legal system and its Screening. Prescriptive and standardized approaches political, administrative, and cultural context play an are two general methods for screening. They are important role in shaping that country?s EIA system, defined and account for differences in EIA systems among legislation and regulations, and discretionary or countries. Figure identified. In some instances, EIA scope is determined 1 presents a framework for screening (UNEP 2002).
Supervision Public of the EIA preparation usually falls either on the Countries vary widely in the extent to which EIA sectoral agency (for example, Peru, Ecuador, US), or relies on public participation, ranging from countries on the environmental agency (for example, Belize), or where opening the decision-making process to citizen is and involvement is one of the main purposes of EIA, to environmental agencies (for example, Argentina). The countries where public participation and involvement environment agency?s role could range from review in the EIA process are not required by EIA regulations and provision of comments about the adequacy of the and rarely practiced. Most countries fall in between, analysis and the impact on the environment, ensuring with regulations that require public involvement at public participation in the EIA, to the approval of the various stages of the EIA process (at screening, EIA, including prior approval of the terms of the scoping, EA preparation, and before and after reference through the screening and scoping stages.EIA preparation. For example, the 2009); EU public directive hearings; was and modified creation to of EIA practitioners in attempts to improve EIA quality (World Bank 2006a; 2006c; 2006f). Project proponents, EIA systems vary in terms of how technical the EIA together with the consultants often hired by them to process is perceived to be, from those where it is seen prepare EIA, have significant effects on EIAs.The capacity of EIA practitioners has systems where the EIA process is seen as more often been cited as an important factor in the quality participatory with respect to public involvement.Advantages and Limitations of Environmental Impact Assessment Public Discussion and Participation. One major strength and outstanding feature of EIA in many Prerequisite Factors for Environmental Impact Assessment countries is increased public discussion and participation (COWI 2009).
However, in practice a In designing or modifying the EIA system, it is number of limitations occur. In some instances where important to have clarity regarding the purpose of the public participation is required by EIA legislation, EIA and what it should and could accomplish within such participation could be limited in practice. For the broader policy framework: whether the need is for example, the law in India required that a public a hearing technical report focused on preparation of is conducted; however, NGOs often mitigation measures for the identified impacts, or considered the public hearing as a staged process that instead for a tool to open the decision-making process appeared to involve citizens when the decision had to already been made.This framework is an In response, the 2006 EIA notification changed the important element in the successful application and requirement from public hearing to public use of EIA (UNU 2011).As evidenced by experiences in El Salvador and In other instances, where projects are only discussed Guatemala (see below), over-reliance on EIA is better openly for their potential environmental merits and avoided; instead, a mix of tools should be utilized to shortcomings, but not for social or economic ones, achieve the goals of environmental management. The public organization responsible for preparation and review environmental problems when there are underlying of EIA needs to have the required capacity for the EIA social or economic reasons for delaying or stopping a system?s intended purpose, to ensure that the public project (World Bank 2006e).The required capacity includes knowledge of Over-reliance on EIA to Achieve Environmental procedures, analytical work, and technical and social Management Objectives. skills. Finally, the availability of baseline data is conjunction with other policy tools and should not be important in implementing and operating an EIA over-emphasized system (UNEP 2002).