Environment Impact Assessment or EIA can be defined as the study to predict the effect of a proposed activity/project on the environment. A decision making tool, EIA compares various alternatives for a project and seeks to identify the one which represents the best combination of economic and environmental costs and benefits.
What is EIA?
Evolution of EIA
History of EIA in India
The EIA process
Forms of impact assessment
Comparative review of EIA procedures and practices
1. What is EIA? Environment Impact Assessment or EIA can be defined as the study to predict the effect of a proposed activity/project on the environment. A decision making tool, EIA compares various alternatives for a project and seeks to identify the one which represents the best combination of economic and environmental costs and benefits.
EIA systematically examines both beneficial and adverse consequences of the project and ensures that these effects are taken into account during project design. It helps to identify possible environmental effects of the proposed project, proposes measures to mitigate adverse effects and predicts whether there will be significant adverse environmental effects, even after the mitigation is implemented. By considering the environmental effects of the project and their mitigation early in the project planning cycle, environmental assessment has many benefits, such as protection of environment, optimum utilisation of resources and saving of time and cost of the project. Properly conducted EIA also lessens conflicts by promoting community participation, informing decision makers, and helping lay the base for environmentally sound projects. Benefits of integrating EIA have been observed in all stages of a project, from exploration and planning, through construction, operations, decommissioning, and beyond site closure.
2. Evolution of EIA
EIA is one of the successful policy innovations of the 20th Century for environmental conservation. Thirty-seven years ago, there was no EIA but today, it is a formal process in many countries and is currently practiced in more than 100 countries. EIA as a mandatory regulatory procedure originated in the early 1970s, with the implementation of the National Environment Policy Act (NEPA) 1969 in the US. A large part of the initial development took place in a few high-income countries, like Canada, Australia, and New Zealand (1973-74). However, there were some developing countries as well, which introduced EIA relatively early - Columbia (1974), Philippines (1978).
The EIA process really took off after the mid-1980s. In 1989, the World Bank adopted EIA for major development projects, in which a borrower country had to undertake an EIA under the Bank's supervision (see table 1: Evaluation and history of EIA).
Table 1: Evolution and history of EIA
Development of EIA
Project review based on the technical/engineering and economic analysis.
Limited consideration given to environmental consequences.
Early/mid – 1970s
EIA introduced by NEPA in 1970 in US.
Basic principle: Guidelines, procedures including public participation requirement instituted.
Standard methodologies for impact analysis developed (e.g. matrix, checklist and network).
Canada, Australia and New Zealand became the first countries to follow NEPA in 1973-1974. Unlike Australia, which legislated EIA, Canada and New Zealand established administrative procedures.
Major public inquires help shape the process's development.
Late 1970 and early 1980s
More formalised guidance.
Other industrial and developing countries introduced formal EIA requirements (France, 1976; Philippines, 1977), began to use the process informally or experimentally ( Netherlands, 1978) or adopted elements, such as impact statements or reports, as part of development applications for planning permission (German states [lander], Ireland).
Use of EA by developing countries (Brazil, Philippines, China, Indonesia)
Strategic Environment Assessment (SEA), risk analysis included in EA processes.
Greater emphasis on ecological modelling, prediction and evaluation methods.
Provision for public involvement.
Coordination of EA with land use planning processes.
Mid 1980s to end of decade
In Europe, EC Directive on EIA establishes basic principle and procedural requirements for all member states.
Increasing efforts to address cumulative effects.
World Bank and other leading international aid agencies establish EA requirements.
Spread of EIA process in Asia.
Requirement to consider trans-boundary effects under Espoo convention.
Increased use of GIS and other information technologies.
Sustainability principal and global issues receive increased attention.
India also adopted the EIA formally.
Formulation of EA legislation by many developing countries.
Rapid growth in EA training.
Source: International Study of the Effectiveness of Environmental Assessment, final report, Environmental assessment in a changing world, Prepared by Barry Sadler, June 1996.
Definition of SEA: Policy tool to assess the environmental consequences of development policies, plans and programmes
Definition of risk assessment: An instrument for estimating the probability of harm occurring from the presence of dangerous conditions or materials at a project site. Risk represents the likelihood and significance of a potential hazard being realized
3. History of EIA in India
The Indian experience with Environmental Impact Assessment began over 20 years back. It started in 1976-77 when the Planning Commission asked the Department of Science and Technology to examine the river-valley projects from an environmental angle. This was subsequently extended to cover those projects, which required the approval of the Public Investment Board. Till 1994, environmental clearance from the Central Government was an administrative decision and lacked legislative support.
On 27 January 1994, the Union Ministry of Environment and Forests (MEF), Government of India, under the Environmental (Protection) Act 1986, promulgated an EIA notification making Environmental Clearance (EC) mandatory for expansion or modernisation of any activity or for setting up new projects listed in Schedule 1 of the notification. Since then there have been 12 amendments made in the EIA notification of 1994.
The MoEF recently notified new EIA legislation in September 2006. The notification makes it mandatory for various projects such as mining, thermal power plants, river valley, infrastructure (road, highway, ports, harbours and airports) and industries including very small electroplating or foundry units to get environment clearance. However, unlike the EIA Notification of 1994, the new legislation has put the onus of clearing projects on the state government depending on the size/capacity of the project.
Certain activities permissible under the Coastal Regulation Zone Act, 1991 also require similar clearance. Additionally, donor agencies operating in India like the World Bank and the ADB have a different set of requirements for giving environmental clearance to projects that are funded by them.
4. The EIA process
The stages of an EIA process will depend upon the requirements of the country or donor. However, most EIA processes have a common structure and the application of the main stages is a basic standard of good practice.
The environment impact assessment consists of eight steps with each step equally important in determining the overall performance of the project. Typically, the EIA process begins with screening to ensure time and resources are directed at the proposals that matter environmentally and ends with some form of follow up on the implementation of the decisions and actions taken as a result of an EIA report. The eight steps of the EIA process are presented in brief below:
Screening: First stage of EIA, which determines whether the proposed project, requires an EIA and if it does, then the level of assessment required.
Scoping: This stage identifies the key issues and impacts that should be further investigated. This stage also defines the boundary and time limit of the study.
Impact analysis: This stage of EIA identifies and predicts the likely environmental and social impact of the proposed project and evaluates the significance.
Mitigation: This step in EIA recommends the actions to reduce and avoid the potential adverse environmental consequences of development activities.
Reporting: This stage presents the result of EIA in a form of a report to the decision-making body and other interested parties.
Review of EIA: It examines the adequacy and effectiveness of the EIA report and provides the information necessary for decision-making.
Decision-making: It decides whether the project is rejected, approved or needs further change.
Post monitoring: This stage comes into play once the project is commissioned. It checks to ensure that the impacts of the project do not exceed the legal standards and implementation of the mitigation measures are in the manner as described in the EIA report.
The overview of the EIA process is represented in figure 1.
Figure 1: Generalised process flow sheet of the EIA process
Source: The manual in perspective, EIA Training Resource Manual, United Nations Environment Programme, 2002
5. Forms of impact assessment
There are various forms of impact assessment such as Health Impact Assessment (HIA) and Social Impact Assessment (SIA) that are used to assess the health and social consequences of development so that they are taken into consideration along with the environmental assessment. One of the forms of impact assessment is strategic environment assessment, which is briefly discussed below:
i. Strategic environment assessment Strategic Environment Assessment (SEA) refers to systematic analysis of the environmental effects of development policies, plans, programmes and other proposed strategic actions. This process extends the aims and principles of EIA upstream in the decision-making process, beyond the project level and when major alternatives are still open. SEA represents a proactive approach to integrating environmental considerations into the higher levels of decision-making.
Despite its wide use and acceptance, EIA has certain shortcomings as a tool for minimising environmental effects of development proposals. It takes place relatively late at the downstream end of the decision making process, after major alternatives and directions have been chosen (see table 3: Difference in EIA and SEA).
Table 3: Difference in EIA and SEA
Environment impact assessment
Strategic environment assessment
§Takes place at end of decision-making cycle
§Reactive approach to development proposal
§Identifies specific impacts on the environment
§Considers limited number of feasible alternatives
§Limited review of cumulative effects
§Emphasis on mitigating and minimizing impacts
§Narrow perspective, high level of detail
§Well-defined process, clear beginning and end
§Focuses on standard agenda, treats symptoms of environmental deterioration
§Takes place at earlier stages of decision making cycle
§Pro-active approach to development proposals
§Also identifies environmental implications, issues of sustainable development
§Considers broad range of potential alternatives
§Early warning of cumulative effects
§Emphasis on meeting environmental objectives, maintaining natural systems
§Broad perspective, lower level of detail to provide a vision and overall framework
§Multi-stage process, overlapping components, policy level is continuing, iterative
§Focuses on sustainability agenda, gets at sources of environmental deterioration
Source: EIA Training Resource Manual, 2nd edition, 2002, United Nations Development Programme
SEA had limited development and implementation till 1990. However, after 1990, a number of countries in developed economies adopted SEA. Some countries such as Canada and Denmark have made provision for SEA of policy, plans and programmes separately from EIA legislation and procedure. Other countries such as Czech Republic, Slovakia, etc have introduced SEA requirements through reforms in EIA legislation and in case of United Kingdom through environmental appraisal. While in New Zealand and Australia, it is a part of resource management or biodiversity conservation regimes. The adoption of SEA is likely to grow significantly in the coming years especially with directives by European Union and Protocol to the UNECE Convention on Transboundary EIA by signatory countries (with a provisional date of May 2003 for completion).
6. Comparative review of EIA procedures and practices
EIA in developing countries
EIA in India
Well-framed EIA legislation in place. For instance, in Canada, Canadian Environmental Assessment Act regulates EIA while EU countries are guided by Directive on EIA (1985).
Lack of formal EIA legislation in many developing countries. For instance, EIA is not mandatory in many African countries
Formal legislation for EIA. It has been enacted by making an amendment in the Environment Protection Act 1986.
In developed countries, active involvement of all participants including competent authority, government agencies and affected people at early stages of the EIA. This makes the process more robust and gives a fair idea of issues, which need to be addressed in the initial phase of EIA.
Limited involvement of public and government agencies in the initial phases. This often results in poor representation of the issues and impacts in the report, adversely affecting the quality of the report.
Limited involvement of public and government agencies in the initial phases.
Integrated approach to EIA followed. All aspects including social and health taken into account.
Mainly environmental aspects considered. Poor on social or health aspects.
No provision in place to cover landscape and visual impacts in the Indian EIA regulations
Proper consideration of alternatives in EIA
The consideration of alternatives in developing countries is more or less absent.
Same as developing countries
The process of screening is well defined. For instance, in EU countries competent authorities decide whether EIA is required after seeking advice from developer, NGO and statutory consultees. In Japan, screening decision is made by the authorizing agency with respect to certain criteria. In Canada, federal authority determines whether an environmental assessment is required or not.
In developing countries, screening practice in EIA is weak. In most cases, there is a list of activities that require EIA but without any threshold values.
Screening done on the basis of a defined list. Threshold values on the size of the project has been used to decide whether the project will be cleared by the state government or the central government.
Scoping process is comprehensive and involves consultation with all the stakeholders. In many countries like US, Netherlands, Canada and Europe, the involvement of the public and their concern are addressed in the scoping exercise. Besides this, funding organisations such as World Bank, ADB and ERDB have provision for consultation with the affected people and NGOs during identification of issues in scoping exercise.
Scoping process in most developing countries is very poorly defined. In many countries including China, Pakistan, etc. there is no provision for scoping. In some countries like in Nigeria and Indonesia, a term of reference is followed for scoping while in some countries like Ghana, Taiwan and Chile, a general checklist is followed. In countries where it is undertaken, there is no public consultation during scoping. Moreover, in most developing countries, scoping is often directed towards meeting pollution control requirements, rather than addressing the full range of potential environmental impacts from a proposed development.
Earlier scoping was done by consultant or proponent with an inclination towards meeting pollution control requirements, rather than addressing the full range of potential environmental impacts from a proposed development. However, the new notification has put the onus of scoping on the expert committee based on the information provided by the proponent. Consultation with public is optional and depends on the discretion of the expert committee.
Most reports in local language
Most reports in English and not in the local language.
Most reports in English and not in the local language. In some case, executive summary is translated into local language.
A multi-disciplinary approach. Involvement of expert with expertise in different areas.
Lack of trained EIA professionals often leads to the preparation of inadequate and irrelevant EIA reports in developing countries
Same in India. Preparation of EIA is done by consultants. Therefore, the selection criterion for the organisation is fees/cost rather than the expertise of EIA team.
Two tier of EIA review, One conducted after the completion of EIA to check the adequacy and effectiveness of EIA and the second done before decision-making.
Poor review or monitoring.
In India too, EIA review is not upto the marks. The review agency called Impact Assessment Agency (IAA) lacks inter-disciplinary capacity. No representation of NGO in IAA, which is a violation of the EIA notification.
Expertise in EIA: The International Association for Impact Assessment (AIA) and other organisations demonstrate that there are a large number of individuals with the capability to design, conduct, review and evaluate EIAs from countries of the North. The major portion of teaching about environmental assessment also takes place in industrial countries.
The expertise in EIA is slowly developing. In most cases, students from the developing countries go to the developed countries to gain knowledge of the subject.
Expertise in this area is developing.
Source: Compiled by Industry & Environment Unit, Centre for Science & Environment, 2006
The fast growing economy, rapid industrialisation and growing urban population in India along with increasing wastewater generation are reasons for concern and reiterate the need for appropriate water management practices. Centre for Science and Environment recognises this need and has developed a five-day hands on training programme aimed at giving practical exposure to participants on wastewater treatment for industrial and urban wastewater management including reuse and recycle.