ENVIRONMENTAL IMPACT
ASSESSMENT
         Dr.S KARTHIKEYAN, M.E., Ph.D
              Associate Professor,
        Centre for Environmental Studies,
            Anna University, Chennai
            Mobile: + 91-9884612135;
          E-mail: ksingaram@gmail.com
Environmental Impact Assessment
  the  history
  its philosophy
  the legislation
  the procedure
  case examples
Environmental Impact Assessment
  the  history
  its philosophy
  the legislation
  the procedure
  case examples
Environmental Impact Assessment
   Before the First World War, rapid industrialization and urbanization in
    western countries caused rapid loss of natural resources.
   Continued after the Second World War giving rise to concerns for pollution,
    quality of life and environmental stress.
   As a result of this, pressure groups formed with the aim of getting a tool
    that can be used to safeguard the environment in any development.
Environmental Impact Assessment
 First introduced in USA
 National Environmental Policy Act (NEPA) became law on January 1, 1971
 Established environmental quality as leading national priority by stating a
   national policy for the environment;
 Made environmental protection mandate of all federal agencies
 Established a Council on Environmental Quality in the Office of the
   President
NEPA (USA, 1971)
   Requires federal agencies to prepare an Environmental Impact Statement for major
    actions or projects that can affect the environment;
Impact Statements must contain:
   A description of the proposed action, its purpose, and description of the environment
    affected
   The relationship to land use plans, policies, and controls for the affected areas;
NEPA (USA, 1971)
   The probable environmental impacts, positive and negative, direct and indirect, and
    possible international implications;
   A discussion of alternatives;
   The probable negative impacts that cannot be avoided or mitigated; The relationship
    between local and short-term use and long-term considerations;
   An irreversible commitments of resources;
   A description of federal actions to mitigate and offset adverse effects
   Comments from reviewers.
Environmental Impact Assessment
  EUROPEAN IMPLEMENTATION
    In 1977 the European Commission began drafting a directive on EIA and
     finally published a proposal in 1980
    Directive 85/337/EEC on the assessment of the effects of certain public and
     private projects on the environment – the ‘EIA Directive’ was adopted in July
     1985 and Member States had until 3 July 1988 to implement its requirements
The EIA Directive
   The EIA Directive requires projects likely to have significant effects on
    the environment by virtue of their nature, size or location to undergo an
    environmental assessment before the competent authority in question
    grants consent
   The EIA Directive defines a project as the execution of construction
    works or of other installations or schemes, other interventions in the
    natural surroundings and landscape including those involving the
    extraction of mineral resources
THE EIA DIRECTIVE
   The EIA should identify, describe and assess the direct and
    indirect effects of a project on the following factors:
       human beings, fauna and flora
       soil, water, air, climate and the landscape
       material assets and cultural heritage
       the interaction between the above factors
   EIA should therefore have a strong social dimension
    Development consent means:
   the decision of the competent authorities which entitles the
    developer to proceed with the project.
     THE EIA DIRECTIVE
Mandatory assessment:
   crude-oil refineries
   thermal power stations and combustion installations (> 300 MW) and nuclear
    power stations
   permanent storage and final disposal of radioactive waste
   cast iron and steel works
   extraction, processing and transformation of asbestos (various size limits)
   integrated chemical installations
     THE EIA DIRECTIVE
Mandatory assessment:
   construction of motorways, express roads and lines for long-distance railway
    traffic, airports with basic runways
   ports and inland waterways which permit vessels
   waste disposal (incineration, chemical treatment or land fill) of toxic and
    dangerous wastes.
THE EIA DIRECTIVE
Optional
   agriculture               food industry
   extractive industry       textile, leather, wood and paper
   energy industry           rubber industry
   processing of metals      infrastructure projects
   manufacture of glass      others
   chemical industry
THE EIA DIRECTIVE
infrastructure projects:
   industrial estate development projects
   urban development projects
   sky lifts and cable cars
   construction of roads, harbors, and airfields
   canalization, flood relief works
   dams and other water storage
   tramways, railways, underground
   oil and gas pipelines …. etc.
Environmental Impact Assessment
Belgium   1985   Italy       1988
Denmark 1989     Netherlands 1986
Germany 1990     Portugal    1990
Greece    1990   Spain      1986
Ireland   1990   UK          1990
Environmental Impact Assessment
  the  history
  its philosophy
  the legislation
  the procedure
  case examples
Environmental Impact Assessment
   Systematic process to identify potential positive and
    negative impacts on the environment (physical,
    biological, socio-economic, cultural) associated with
    proposed activity
   Examine alternatives / management measures to
    minimize   negative    and  optimize  positive
    consequences
   Prevent substantial detrimental effects to the
    environment
Environmental Impact Assessment
   EIA is defined as a systematic process to identify, predict and
    evaluate the environmental effects of proposed actions and
    projects. This process is applied prior to major decisions and
    commitments being made, and particular attention is given
    in EIA practice to preventing, offsetting and mitigating the
    significant adverse effects of proposed undertakings
Environmental Impact Assessment
EIA is as a preventive measure.
It gives environmental considerations equal weight
with technical, Social and economic aspects.
Public participation ensures acceptance of projects
implemented.
Environmental Impact Assessment
   the  history
   its philosophy
   the legislation
   the procedure
   case examples
EIA NOTIFICATION 2006
   Prior Environmental Clearance is Mandatory
   Applicant has to submit Form 1 & 1A to EAC / SEAC
   Four Stages
   Screening
        Category ‘A’ ‘B1’ and ‘B2’
        B2 does not require EIA study
   Scoping
   Terms of Reference will be prescribed by EAC / SEAC
   Then conduct EIA study and prepare draft EIA report
   Public Consultation Meeting
   Apply to Member Secretary of Concerned SPCB
   Conduct Public Consultation Meeting
   Appraisal
   Present the project, EIA findings and get clearance
Environmental Impact Assessment
   the  history
   its philosophy
   the legislation
   the procedure
   case examples
                              Stages of EIA
 Screening       (does the project         Impact assessment
          require EIA?)                       (interpreting the impacts)
 Scoping      (what issues and           Mitigation       (what can be done to
impacts should the EIA address?)              alleviate negative impacts?)
Baseline studies (establish               EIS preparation/review
   the environmental baseline)                (document the EIA findings)
 Alternatives        (consider the         Public consultation
      different approaches)              (consult general public and NGOs)
Impact prediction        (forecast       Monitoring (monitor impacts
   the environmental impacts)                        of project)
                        Screening
   Is an EIA needed?
   Projects may have no significant environmental
    effects
   A screening mechanism to identify those projects with
    potentially significant adverse environmental effects
                       Scoping
   The scope of an EIA is the issues and impacts it
    addresses
   Scoping is the process of deciding which of a project’s
    possible alternatives and impacts should be
    addressed in the EIA
   An EIA should focus only on the significant issues and
    impacts
                Baseline studies
   Current status of the environment
   The baseline study should anticipate the future
    state of the environment assuming the project is not
    undertaken - the ‘no action alternative’
   This provides the ‘baseline’ against which future
    impacts can be assessed
   Should be undertaken for each alternative site
                              Alternatives
   EIA is ideally undertaken for a project and its alternatives
   e.g. different locations, scales, designs & even the raw materials
         Impact Prediction
   Using Models or professional Experience,
    forecast the impact
                       Impact assessment
   evaluating the significance of the impacts identified
   Significance determined through professional judgement, reference to
    regulations etc.
   The conclusions of the impact assessment can ultimately be used by
    decision-makers when determining the fate of the project application
   Potential for bias in determining what is significant
     Types of impacts & their attributes
 Direct & indirect impacts    Intensity
                               Direction
 Short-term & long-term
  impacts                      Spatial extent
                               Duration
 Adverse & beneficial
  impacts                      Frequency
                               Reversibility
 Cumulative impacts
                               Probability
                         Mitigation
   Negative impacts on the environment identified during the EIA can
    be alleviated through mitigation measures
   Mitigation hierarchy: Avoid - Reduce - Remedy - Compensate -
    Enhance
   Impacts remaining after mitigation are known as residual impacts
               EIS preparation / review
   The Environmental Impact Statement (EIS) is a formal document which
    includes information on the development and information relating to
    screening, scoping, baseline studies, alternatives etc.,
   Common requirement to include a non-technical summary
                EIS preparation / review
   Once complete, the EIS is submitted to the competent authority (along
    with the planning application)
   The EIS is often reviewed (either formally or informally)
   The review enables the competent authority / reviewer to decide
    whether the EIA is adequate, accurate and unbiased
                    Public consultation
   The EIA Notification requires public consultation on the application
    for development and the EIS
                  Post-project monitoring
   Monitoring should determine:
       the accuracy of the original predictions
       the degree of deviation from the predictions
       the possible reasons for any deviations
       the extent to which mitigation measures have achieved their objectives
       What are the improvements required?
Environmental Impact Assessment & Project
                  Cycle
                  Advantages of EIA
   To authorities:
      Decision   making;
      Improvement     / protection of environmental
       quality;
      Management      to   sustainable   utilization   of
       resources;
                Advantages of EIA
   To interested and affected parties
      An   opportunity to be heard;
      Protecting    environmental rights;
      Increasedknowledge and environmental
       awareness
      Utilization   of local and indigenous knowledge;
                      Advantages of EIA
   To developers:
          Proactively   asking the right questions
          Adequacy    of natural resources
          Risks   associated with environmental factors (geologic
          stability, hydrology regimes, fire, etc)
          Pollution   potential and prevention
          Energy    and water saving and associated financial savings
          Appropriateness    of activity in terms of strategic planning
                       Limitations of EIA
   ToR are poorly drafted
   Potentially serious issues are not assessed
   Delays in project approval and cost increases
   EIA report is incomplete or not scientifically-defensible resulting either in
    project rejection or extended delays to address deficiencies
   Susceptible to bias and personal interests (developer as well as
    pressure groups)
   Quality of data (out of date or the level of detail may be insufficient)
                     Types of EIA
Project-level EIA:
       Examines potential environmental impacts of a single    project
or activity
Cumulative effects assessment (CEA):
     Examines potential impacts of multiple projects
Strategic environmental assessment (SEA):
       Involving systematic evaluation of potential impacts of policies,
plans and programs (PPP)
Rapid Environmental Impact Assessment
Comprehensive Environmental Impact Assessment
               METHODS OF EIA
   Ad hoc
   Checklists
   Matrices
   Networks
   Overlays (GIS)
Ad hoc Method
useful when time constraints and lack of information require
    that the EIA must rely exclusively on expert opinion
   Experts opinion
   No scientific analysis and Conclusion
   Easy, takes less time
   Cannot be considered for decision making
Descriptive Checklist
Weighting and Scaling Techniques
                           Example Network
Urban                     Increase in                             Increased fresh
                                              More Run-off
Development               Paved Area                              water estuary
                                        Loss of Aquifer           Reduction in
                                        Recharge                  Estuary Salinity
               Go for private water      Loss of Drinking Water   Decrease in Growth
               source                    in wells                 and size of Shellfish
              Cost of Water goes up                               Biodiversity of Estuary
                                                                  Ecosystem reduces
                                                                  Reduction in Fishing
                                                                  Activity
                                        CHANGING QUAL IT Y                                                                                                  CHANGING QUAL IT Y
                                       OF LIFE FOR W IL DLIFE                                                                                                 OF TOURISM
                                       Lo ss o f Ha bi t at                                      Inc re a se d Inc i de nt s
                                                                                                 b et we en                                                          Lo ss o f Na t ural
                                                                                                 Wi ld l ife & Peo p le                                              Wi ld e rn ess Val u e
De forest at i on &            Ero si o n of            Ri v er Ba nk         Ov erg ra z in g                                 Ch an g es in
Lo ss o f Bi o di ve rsi t y   Go rge                   Ero si o n            Aro un d
                                                                                                                               An i mal Be ha vi o ur
                               Ac ce ss Pat hs                                Wa te r Hol es
                                                                                                   To o sma ll an area
                                                                                                   for an im al nu mb ers
                                                                      Ri p ari an                  Co nst ric t io n                                    Ha rra ssm en t
Sel ec t iv e Cu t ti n g                                                                          o f wi l dl i fe
o f t re es for                           Wa te r           Wa ve Ve ge t at i on                                                                       o f wi l dl i fe
                                          Pol lu t io n     Effec t s Re du c ed                   mo ve me nt s
Cu rio Woo d
                                                                                                    Mo re Fe nc es/               Vi sua l Di stu rba nc eInc re a si n g
                                         Oi l y d isc ha rg es        Ri v er Ba nk & Isla nd       En cl o su res                Impa c ts o f wi l dl i fe n oi se le v el s
                                         fro m bo a ts et c.          De ve l op me nt
                                                                                                                                                                                              Ne w Ro a d
De ma nd fo r                                                                                      Ex pa n si o n of                                      Mo re Ai rcraft        Mo re        & Bri dg e a t Ol d
                                Mo re                Mo re
Cu rio s                        Ra fti n g           Jet t ie s &                                  Ho t el s/C amp s                                      Fly in g Ove r         Mo to r      Dri ft / Za mb ez i
Inc re a se d                                                                                      & To uri st Fa c il i ti e s                           Fal ls & To wn         Ve hi c le s Na t io na l Park
                                Li c en ce s         Bo at Li c en ce s
                                                                                                 Inc re a se d Vi si to r Numb e rs
            De ma nd fo r                        Mo re Di rec t               Impro ve d Bo rde r                                               Impro ve d Ro a d Li nk s
            Lo w-spe nd i ng                     Int ern at i on al           Fac il i ti e s                                                   - L iv i ng sto n/ Lu sak a
            To uri sm In cre ases                Fli gh t s                                                                                     - Z am bi a/ Bo t swan a/ Nami b ia
                                                                              Inc re a se d c ust oms co -op erat i on
                                                 Ai rpo rt Up gra di n g      b et we en Zi mba b we/ Z amb i a
                   Overlay Maps
   Separate mapping of critical environmental features
    at the same scale as project's site plan
       e.g. wetlands, soils, floodplains, bedrock outcrops, wildlife
        habitats, vegetative communities, and cultural resources...
   Older Technique: environmental features are
    mapped on transparent plastic in different colors
   Newer Technique: Geographic Information Systems
    (GIS)
                Overlay Maps
   Advantages
       maps are commonly available
       Excellent for showing spatial dimension and
        location of impacts
       Most useful for assessing alternative routes for
        linear developments, e.g. pipelines, roads,
        transmission lines
   Disadvantages
       Less successful with timing, reversibility, and
        probability of impacts
       Sharp boundary definitions can be misleading