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Title: PENTAWII Workshop on Environmental Assessment Curriculum


1
PENTA-WII Workshop on Environmental Assessment
Curriculum
EIA policies and processes THE
THREAT PERSPECTIVE
  • Prepared by
  • Dr Prafulla Soni, Chairperson
  • Dr. Indra N. Sinha, Member
  • Dr. Ajay K. Lal, Member
  • Mr. Vipin Sahni, Member

2
Policy Issues
  • Political Will ?
  • EIA initially introduced (1982)
  • To fulfill donor agency requirements
  • To comply with PIB Rules
  • To cope with mounting internal pressure after
    Bhopal disaster(1985)
  • Judicial Activism
  • Took 12 years to give it legal standing
  • THREAT
  • It would be difficult to put in place an
    appropriate EIA system
  • REMEDY
  • ?????? Who will bell the cat?
  • Awareness campaign

3
Policy Issues
  • Lack/Inadequate EIA Capacity Building
  • Acute shortage of skilled EIA professional
  • Acute shortage of EIA trainers
  • No focused research on EIA Methodology/ Technique
  • EIA techniques are obsolete/ outdated/
    mechanistic
  • No attempt to internalize environmental costs
    into environmental decision making

4
Policy Issues
  • Non-inclusive and unbalanced economic growth
  • Less developed people/ regions demand development
    projects
  • Consider EIA as deterrent to development activity
  • Resistance to EIA

5
Policy Issues
  • Inability to consider environmental issues
    against a holistic perspective
  • Biased and/or unrealistic EIA

6
Policy Issues
  • Lack of interdisciplinary approach
  • Receiving environment is not considered as an
    assemblage of interacting environmental
    attributes
  • Projects are not considered as an ensemble of
    linked activities in a space-time framework
  • Activity-attribute interactions are not given due
    considerations
  • Poor Impact Prediction and assessment

7
Policy Issues
  • Wide gap in Indian and international
    environmental standards
  • Inability to meet international standards
  • In future course correction may have to be done
    through retro-fitting activities
  • Future non-viability of projects

8
Policy Issues
  • Globalization conflict of interest
  • Rising role of global players in domestic market
  • Ability to Influence national decisions

9
Policy Issues Crisis of perception
  • Definition galore leading to confusion
  • 'a process to predict and consider both positive
    and negative environmental and social
    consequences of a proposed development project'
    (UNEP 1994).
  • 'an assessment of all relevant environmental and
    resulting social effects which would result from
    a project' (Battelle Institute 1978).
  • 'in establishing quantitative values for selected
    parameters which indicate the quality of
    environment before, during and after an action
    Heer and Hagerty (1977)

10
Policy Issues Crisis of perception
  • Resulting confusion
  • These definitions often look towards EIA as a
    project level activity
  • The word environment is often not clearly set,
    leaving options wide open to include everything
    from a very small (project boundary) to a very
    large (the entire biosphere) area.
  • EIA is at best a process, enabling relative
    ranking of projects against environmental
    desirability point of view.
  • The environmental desirability is limited to
    short term 'standard' attainment and little or no
    emphasis is placed on the long-term goal of
    attaining environmental sustainability
  • THREAT
  • EIA shall not become a planning tool and shall
    not contribute towards attaining environmental
    sustainability

11
Policy Issues Crisis of perception
  • REMEDY
  • Accept revised definition of EIA
  • EIA is a process to improve decision making and
    to ensure that the project/ programme options
    under consideration are environmentally and
    socially sound and sustainable (Roe et al. 1995)
  • EIA is 'a process of environmental planning that
    provides a basis for resource management to
    achieve the goal of sustainability' (Smith 1993)

12
Policy Issues Crisis of perception
  • Environmental Impact Assessment is a systematic,
    reproducible and interdisciplinary study for
    evaluation of the potential changes in the
    natural capital stock (in terms of resource
    supply and waste assimilation capabilities)
    likely to occur due to a proposed or impending
    human activity or any of its feasible
    alternatives, and an evaluation of possible
    mitigation measures to ensure long-term
    environmental sustainability (Sinha 2001)

13
Policy Issues Crisis of perception
  • No tiered approach to EIA
  • SEA not adopted (Policies, Plans, Programmes not
    subjected assessment)
  • Cumulative Effects assessment not in practice
  • THREAT
  • EIA can not become an effective instrument for
    sustainable development

14
Policy Issues Crisis of perception
  • REMEDY
  • EIA should be tiered in the following way.
  • Screening economic and development policies for
    their conformity with sustainability goals and
    principles.
  • Preliminary assessment of environmental costs of
    development programmes to identify low-impact,
    resource efficient energy, transportation and
    other sector strategies.
  • Area wise assessment to establish resource values
    and land-use capabilities for regional
    development.
  • Project EIA to identify in-kind compensation for
    natural capital losses (e.g. Affecting residual
    fish and wildlife losses by ex-situ habitat
    rehabilitation and enhancement).
  • Strategic Environmental Assessment may be made
    mandatory. EU directive may act as a guide

15
Policy Issues Crisis of perception
  • Constitutional Provisions
  • the State shall endeavour 'to protect and improve
    the environment' and 'to safeguard the forests
    and wildlife of the country' (Article 48A)
  • It is the duty of every citizen of India 'to
    protect and improve the natural environment
    including forests, lakes, rivers and wildlife and
    to have compassion for living creatures' (Article
    51A(g))
  • THREAT
  • The Constitutional provisions are not binding on
    companies as according to a SC judgment a company
    is not a citizen of India

16
Policy Instruments Crisis of Intent
  • Major policy resolutions affecting EIA
    effectiveness include
  • Indian National Forest Policy 1988
  • Statement on Industrial Policy 1991
  • National Conservation Strategy and Policy
    Statement on Environment and Development 1992
  • Policy Statement for Abatement of Pollution 1992
  • National Mineral Policy 1993
  • National Environmental Policy, 2006
  • National Education Policy 1986 (as revised later)

17
Policy Instruments Crisis of Intent
  • Policy Instruments are high on rhetoric and low
    on action component
  • EXAMPLE
  • Mining operations will not ordinarily be taken
    up in ecologically fragile areas. Every mining
    project shall be accompanied by a mining plan
    including an environmental management plan and
    time bound reclamation programme for controlling
    the environmental damage and for restoration of
    mined areas (Policy Statement for Abatement of
    Pollution, 1992)
  • In reality it required an active judiciary to set
    the things right
  • The Environment Action Programme (1993) promised
    setting up of a National Centre for Training in
    EIA and also a network of regional EIA training
    centres
  • Had appropriate action been taken, this workshop
    would have become redundant

18
EIA Processes Inadequacies
  • EIA is viewed both as either science or art but
    not both
  • The 'art' of EIA aims at aiding the
    decision-making process by attempting analyses of
    actions and consequent impacts
  • Identification, prediction and evaluation of
    environmental impacts fall in the realm of the
    'science' of EIA
  • This tunnelled vision adversely affects EIA
    effectiveness

19
EIA Processes Inadequacies
  • Proponents prepare EIA
  • He who pays the piper draws the tune
  • EIA reports are essentially advocacy documents

20
EIA Processes Inadequacies
  • Cluster of small projects may not require
    comprehensive EIA after IEE although total
    adverse impacts may be significant
  • REMEDY
  • Screening criteria, introduced in 2006, may be
    revised to incorporate cumulative effects
    assessment

21
EIA Processes Inadequacies
  • Scoping
  • TOR prepared by proponent and approved by MoEF
  • No Public Participation
  • high probability of missing out critical issues
  • Basic objective of scoping should be to make the
    EIA report 'balanced and thorough' by identifying
    and studying the real problems and by ensuring
    that issues of no real concern do not consume
    undue time and effort
  • This can be achieved through Public Participation
    at scoping stage

22
Baseline studies
  • Description of environmental baseline does not
    include the establishment of both the present and
    future state of the environment, in the absence
    of the project, taking into account changes
    resulting from natural events and from other
    human activities
  • REMEDY
  • In order to be an effective component of 'EIA as
    a planning tool' the baseline study should be
    modified to include preparation of a pre-project
    environmental inventory so as to suitably
    describe the supportive and assimilative capacity
    of the environment. It is also important to
    understand the natural interaction between the
    various environmental elements and the functional
    relationships involved
  • It is important that preparation of a
    straightforward environmental inventory be
    complemented by focussing on valued ecosystem
    components (VECs) and by identifying key
    biological processes at the beginning of the EIA
    process

23
Impact Prediction
  • The term "impact" refers to the effects of a
    proposed human actively on both "ecosystem" and
    "human society Dooley (1979), Lee (1982)
  • Prediction models for social impacts are not
    used
  • gt social impact assessment is essentially a
    reflection of apprehensions, expectations and
    cover ups

24
Impact Prediction
  • The 'error of estimate' of impact forecasting are
    significantly high because
  • Standard and sufficient predictive models are not
    used
  • site-specific data are inadequate to support a
    quantitative assessment of environmental impacts
  • No standard or unambiguous criteria is used for
    defining quantitative threshold to distinguish
    between significant and insignificant impacts
  • Non-utilisation of quantitative/ statistical
    methodologies for objectively describing levels
    of impacts
  • The inaccuracy of impact prediction increases
    because of the need for subjective scoring

25
Impact Prediction
  • The intrinsic problems associated with prediction
    of impacts within reasonable degree of accuracy
    make impact prediction 'technically most
    difficult and challenging activity' (Canter 1996)
  • Impact prediction often requires technically
    demanding mathematical models
  • Models are often presented as 'black-boxes',
    containing little information about the model
    arguments
  • This makes the bases for impact prediction
    unclear and the inherent errors become
    untraceable.

26
Impact Evaluation
  • refers to determination of significance of
    predicted impacts against the total quality of
    the affected environment.
  • significance determination invariably involves
    subjective or normative evaluation
  • The main challenge of environmental impact
    assessment resides in analysing and assessing the
    likely impacts within acceptable level of errors
    (Julien 1995).

27
Impact Evaluation
  • Numerous methodologies are in use for impact
    summarisation and aggregation
  • while overall rating definitely facilitates
    comparison of various alternatives, it often
    hides the judgement used in the calculation. The
    decision-maker is, thus, denied access to the
    thought process
  • No standard methodology adopted in India
  • The failure of impact evaluation exercises are
    largely due to inadequate expertise and error of
    intent of the evaluators
  • Care must be taken to ensure that all the
    significant impacts associated with a proposed
    project are fully and adequately taken into
    consideration

28
Impact Mitigation
  • Only end-of-pipe measures are suggested to remedy
    the various impacts associated with projects
  • Measures to avoid, reduce or compensate for the
    various impacts associated with projects are not
    planned

29
Impact Mitigation
  • REMEDY
  • mitigation should include the following.
  • Avoiding the impact altogether by not taking a
    certain action or parts of an action.
  • Minimising impacts by limiting the degree or
    magnitude of the action and its implementation.
  • Rectifying the impact by repairing,
    rehabilitating, or restoring the affected
    environment.
  • Reducing or eliminating the impact over time by
    preservation and maintenance operations during
    the life of the action and,
  • Compensating for the impact by replacing or
    providing substitute resources or environments.

30
Concluding Remarks
  • EIA is focussed on identifying, predicting and
    mitigating bio-physical effects
  • opportunity for public involvement is limited
  • Multi-dimensional EIA, incorporating social
    impact assessment (SIA) and risk analysis be
    introduced
  • public consultation be made an integral part of
    development planning and assessment
  • increased emphasis be laid on issues for
    justification and alternatives in project review.

31
Concluding Remarks
  • Efforts be made to integrate project EIA with
    policy planning and follow up phases
  • Research and development work be carried out on
  • effects of monitoring
  • EIA audit and process evaluation
  • mediation and dispute resolution approaches

32
Concluding Remarks
  • Scientific and institutional frameworks for EIA
    must be rethought in response to sustainability
    ideas and imperatives
  • Research be carried out to find ways to address
    regional and global environmental changes and
    cumulative impacts
  • Advantage be taken of growing international
    co-operation on EIA research and training

33
Concluding Remarks
  • Strategic environmental assessment (SEA) of
    policies, plans and programmes be introduced

34
Threats - Process
  • ScopingInadequate involvement of all
    stakeholders
  • Capacity and capability for
  • Carrying out EA studies
  • Evaluation of EA reports
  • Compliance monitoring

35
THANK YOU
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