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Conclusion on Environment Impact Assessment
(EIA) :
The literature reveals that the EIA Notification contains many of the key
elements found in most processes throughout the world including screening,
scoping, comprehensive study, progress reports, review, decision and
follow-up. However, from the lack of reference to project need, purposes and
alternatives, a reasonable inference is that the process reflects a narrowly
focused, technical approach, rather than the more broad, open and
anticipatory approach called for in some quarters and found in some
countries (Gibson 1993; Wood 1995). In addition, reviews of the
implementation of the notification are somewhat mixed. Banham and Brew
(1996) indicated in their assessment that there is reason to be optimistic
about the use of EA in India. While others, such as Dwivedi (1997) and
Thakur (1997), suggested that the process is still in its early stages of
development and that India lacks many of the institutions and knowledgeable
government officials necessary to make the process work properly. An
important aspect of the 1994 EIA notification is its relation to other
policy instruments in India's environmental management system.
However, a close look at the EIA in India reveals that some improvement
is needed in the following aspects. EIA's are controversial in India because
of little participatory democracy in the formulation and implementation of
environmental legislation. There have been cases where, more than one EIA
for the project has been approved by an authorized agency and subsequently
revoked by judicial action initiated by public interest litigations (The
Hindu Survey of Environment). A fresh outlook at the EIA requirement is
essential, especially a public review, which would help in the development
of a sound normative framework for guiding the entire process. It is also
unclear as to how an EIA is to be prepared, what norms it must satisfy how
it is to be approved. The requirements for EIA in India are generally
comprehensive and include information on land use pollution sources in air,
water and solid waste quality. But the problem arises here because of no
proper set of guidelines for project types covered by the rule. With the
promoter's own assessment, the regulatory authority is to make a judgment if
EIA is complete and if the project meets the environmental standard. It is
quite essential that the regulatory authority periodically review the norm
with scientists, NGOs and industry. Measurement techniques and location
where the standard is to be met are not specified, leaving it for
interpretation from both, the plant engineer and government inspector. This
makes the project promoter to adopt the lenient interpretation of the norms
during EIA preparation. The EIA and environmental clearances fall within the
power of the Center but the implementation of pollution control is with the
states. This leads to a scenario where multiple agencies sharing similar
responsibilities without well defined roles. Some cases of plagiarized
reports by the consultants have been reported in India (The Hindu Survey of
Environment).
Another major improvement required is in the area of public involvement.
There has been dilution of previous notifications especially regarding
public participation. For instance, a recent amendment to the EIA
requirements that was notified on 13 June 2002 exempts pipeline projects
from preparation of EIA reports. This has further weakened the process of
environmental clearance. It also violates the basic premise of authority
granted by the Environment Protection Act, 1986. Yet, public hearings need
to be conducted in all the districts from where the pipeline will pass. This
poses two problems: firstly, it is not clear how an EMP (Environment
Management Plan) and Risk Mitigation measures can be formulated when the
developers have not studied the potential impacts of a proposed pipeline
through preparation of an EIA report. Secondly, on what basis would persons
attending a Public Hearing relating to a pipeline project voice their
concerns? Both the routing and the construction of pipelines can have severe
consequences on people and their environment. Pipeline projects may create
unnecessary hardship to local people due to construction work, and pipeline
leaks are a potential hazard. Both routing and construction can cause
unnecessary and severe damage to sensitive ecosystems. But if these projects
are exempted from the EIA process, no other mechanism ensures adequate
review of these potential consequences. Curiously, the June 2002 amendment
reconstitutes the requirement that EIA reports must be made available to the
public prior to the Public Hearings, a requirement that was done away with
earlier.
There are other examples. The 1994 notification, made it mandatory for
the Impact Assessment Agency (IAA), i.e. the Ministry of Environment and
Forests to consult a Committee of Experts before granting environmental
clearance to a particular project. In its present amended form the
notification states that the IAA may consult the Committee of experts if
deemed necessary. The 1994 notification made it mandatory for half-yearly
compliance reports prepared by the project authorities to be made publicly
available. The notification now leaves it to the discretion of the IAA to
make complaint reports publicly available, "subject to public
interest". Clearly, the recent amendments are resulting in the dilution
of the law on environmental impact assessments. However, for pipeline
project, Environmental Impact Assessment report will not be required. But
Environmental Management Plan including risk mitigation measures are
required."
The case studies coupled with our earlier analyses, demonstrate that
substantive, early investments (during the scoping phase itself) in public
participation can benefit the project proponent, the public and the final
plan. An effective public participation programme does not happen by
accident; it must be carefully planned. As the case studies show, a
proactive effort will lead to a more effective process and outcome than a
reactive, minimalist approach to public involvement. We draw upon the
results of the case studies to provide suggestions for improving public
participation programmes in EIA. First, public involvement needs to begin
before project planning and decision-making are too far along to be
influenced. The decision to participate must be genuine. Otherwise, public
participation becomes a procedural exercise rather than a substantive
democratic process. Second, public involvement can be used to create a
project that is more suitable to, and accepted by, the public. Suitability
should depend on public opinions and needs (rather than the technical
feasibility of the project). Third, public input can be a crucial and
valuable source of expertise before, during and after project planning and
decision-making. Moreover, based on the case study experiences it can be
seen that the EIA legislation must be more explicit in defining the affected
area according to potential socio-economic impacts. Only the authority
competent in evaluating socio-economic effects should be given the
responsibility
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