Module 3
E I A ME T H OD OL O G I ES : AD H O C , CH E C KL I ST ,
   MA TRIX , NE TWO RK A ND ASS ESS MEN T O F
E CO L O G IC A L I M P AC T S AN D SO CI O E CO NO M I C
                        IMPACTS.
                  Socioeconomic impacts
 Socio-economic impacts are the influence of projects and/or
  programmes or policies on the human values, culture, living
  standard.
 Institutions undertaking large investment projects such as
  highways, air ports, sewerage systems, water resources projects
  (reservoirs, water relating systems, diversions, canals) stimulates
  secondary impacts in the form of associated investments and
  changes in socio-economic activities.
 These effects include changes in the existing community
  facilities and activities, induce new facilities in the next round
  and changes in natural conditions. All such effects may be
  substantial than the primary impacts of the original actions.
   SOCIO-ECONOMIC IMPACT ASSESSMENT
             METHODOLOGY
 Step 1. Identification of potential socio-economic
  impacts for assessment.
 This is to identify the basic indicators to assess the
  environmental impacts of all kinds (air pollution, water
  pollution, noise pollution) which will effect human quality
  of life Other important factors will be
 demographic factors – population, density, literacy
 economic variables – land use patterns, income levels, price
  levels, employment/unemployment level, commercial
  activities
 social variables – patterns of life and work, ethnic
  composition, religious and tribal factors, public utilities
 project specific variables – displacement, business,
  recruitment of manpower, project technology
 Step 2. Description of existing socio-economic or
 human environment of the project area Developing a social
 profile based on siting of projects
 Step 3. Procurement of relevant standards, criteria and
  guidelines
There are direct effects of pollutants/emissions on the public and
whenever people are affected, health and welfare socio economic
considerations become important
 Step 4. Prediction of Socio-economic Impacts
 Prediction of Socio-economic Impacts with or without the project is an
  important technical exercise. There is no unique method for
  predicting the impacts yet four approaches are indicated:
➢ qualitative description
➢ quantitative description
➢ application specific prediction technique (may involve survey from
 secondary sources or qualitative descriptive approach like Delphi
 method or Historical analogies
➢ comparison of the effects of alternatives
 Step 5. Assessment of Socio-economic Impact
 Assessment of socio-economic impacts with or without project in its surrounding
    areas is difficult as there are no established standards for these. Some impacts
    may be clearly visible and assessable such as:
➢    generation of employment for local people (+ve impact)
➢     increase in earnings of people (+ve impact)
➢   pressure on local services (-ve impact)
➢     increase in business and trade (+ve impact)
➢   increase in crime rate in the region (-ve impact)
➢    interaction with outside people (+ve impact)
➢     opening of attitudes of people (+ve impact)
 Step 6. Mitigation Measures
 Though there is very little in the form of mitigation measure to
  reduce the adverse socio-economic impacts of the project.
 However, Some local benefits, particularly employment of the
  local people, rehabilitation and resettlement of project affected
  people will be mandatory by law.
 The project is a user of local resources and in lieu it has to give
  back some benefits to the local population otherwise they resent
  its activities and the project functioning is jeopardized.
 Mitigation measures will include, providing housing schools,
  colleges, hospital, power and other social services.
    IMPACT ASSESSMENT METHODOLOGY
   Choice of a Methodology
➢ Use: Whether the document is for information or a decision document       The decision
    document requires more details and greater emphasis is on key issues, quantification and
    comparison of alternatives.
➢    Alternatives: Much would depend on what alternatives to the project are available since
    these would require a more thorough quantification and comparison.
➢    Public involvement: The role of stake holders and their participation may also require
    issues which are relevant and need discussion and thus details.
➢    Resources: What resources are available for the document preparation in terms of
    experts available, data, time and money.
 Familiarity: Familiarity with ground conditions will also be
  a keen element. Greater familiarity will improve the validity
  of subjective significance.
 Issue significance: If the issues involved are larger then
  more details are needed, quantification is important and
  hence the choice
 Administrative: Are the documents being prepared are
  dictated by procedure of implementing agency
                  1.AD HOC method
 Simple method based on subjective assessment of
  environment impacts on broad aspects.
 Ad hoc method is useful when time constraints and lack of
  information require that the EIA must rely exclusively on
  expert opinion.
 It provides minimal guidance for total impact assessment
  while suggesting the broad areas of possible impacts and the
  general nature of these possible impacts.
 When more scientific methods are available, it is not
  recommended.
               Types of Ad hoc method
 Opinion polls.
 Experts opinion.
 Delphi methods (The Delphi method is a forecasting process
 framework based on the results of several rounds of
 questionnaires sent to a panel of experts. Several rounds of
 questionnaires are sent out, and the anonymous responses are
 aggregated and shared with the group after each round. The
 experts are allowed to adjust their answers in subsequent
 rounds. Since multiple rounds of questions are asked and the
 panel is told what the group thinks as a whole, the Delphi
 method seeks to reach the correct response through consensus)
 Advantages
 Specialists on a particular area will provide guidance.
 Disadvantage
 It requires expert.
 Short/long term impact are merely examined on guess
  basis.
 Identification, prediction and interpretation of impacts are
  quite poor
THE CHECKLIST METHOD
CHECK       +   LIST        =
                       CHECKLIST
        +                =
                     Checklist Method
 Checklist means a listing of potential Environmental
  Impacts.
 This method is done to assess the nature of the impacts i.e.
  its type such as adverse /beneficial, short term or long term,
  no effect or significant impact, reversible or irreversible etc.
 Environmental       Impact     Assessment
 Checklist is a list of items that has to be
 checked or done to anticipate the
 environmental       consequences    of    a
 development before planning permission is
 granted.       Environmental        Impact
 Assessment Checklist are designed to
 establish whether a proposed project is
 likely to have negative impacts on the
 environment
 There are 4 types of Checklist : simple
 checklist, weighted-scale checklist, forced
 choice checklist and descriptive checklist.
Checklist method - Example
                  Simple check list
 It includes certain statements of yes or no type.
 In simple checklist method, equal
 importance or weightage is given to all
 the statement.
 Simple Lists.
 ➢   Presents a list of parameters related to the project
 ➢   No guidelines on how to interpret and measure the parameter
 ➢   Does not help in decision making
 ➢   No information on cause effect relationship
 ➢   Strong in impact identification
 ➢   No information needed on magnitude or importance of impacts"
 ➢   List of parameters without guidelines provided on how to
     interpret and measure an environmental parameter.
             Weighted scale checklist
 Weights are assigned to different statements to
 indicate their importance.
FORCED CHOICE CHECKLIST
In this method, the raters are given a set
of multiple choice        (forced choice)
questions, from which they are to select
one option and rate the statement.
This list contains only positive or
negative sets of readymade choices of
behaviors to choose from.
                     Descriptive checklists
 Descriptive checklists   include list of environmental factors along with
  information on measurement, impact prediction and assessment.
• This   provides more information on           nature and magnitude of
  impacts rather than just identifying whether they would occur or not.
• The information within each box can be quantitative or qualitative.
• The identification of the incidence of cumulative impacts is again
  essentially reliant upon expert opinion.
Descriptive checklist
                  Descriptive checklists
•   Checklists are very descriptive and focus on details about methodology
•    Generally used by decision makers during project appraisal.
•   Simply identify the possible potential impacts without any rating regarding
    their relative magnitudes
                   Questionnaire Checklist
• Checklist prepared based on the questions asked.
• This is used mainly for Public Consultation; it tells about the
  stakeholders awareness and responses towards the proposed project.
• The questionnaire is then further evaluated in spread sheets to find
  the scale of impacts and weight of parameters based on public
  opinion.
Questionnaire check list
ADVANTAGES OF CHECKLIST
Encourages discussion during the
initial stages of assessment.
Helps to ensure that the vital impacts
are not neglected.
Checklists may also help to produce
a higher degree of awareness of the
environmental aspects of a project.
Quantification of impacts is possible
using the weighted-scale method.
                      DISADVANTAGES
 Do not distinguish between direct and indirect impacts.
 They are too general or incomplete
 Lack of detailed information because of ready made options
 Time consuming and trained people are required.
 The identification of effects is qualitative and subjective.
   The main drawback of the checklist method is the inability to
    relate individual activities to environmental components
    affected by these activities
                       Matrix Method
   Matrix are two-dimensional tables which facilitate the
    identification of impacts arising from the interaction between
    project activities and specific environmental components.
  Identifies interaction between Project actions- Environmental
  Parameter
 Gives information on cause effect relationship
 Environmental items (Y axis) and Project actions (X axis)
 The relationship between Action & Env. Parameter will be given
  at the intersection
    TYPES OF MATRIX
1    Simple Matrix     Weighted Matrix
                                   5
        Time          Quantified Matrix
     dependent       (Leopold Matrix)
     2 matrix                     4
            Magnitude
            Matrix
                 3
 SIMPLE MATRIX
2-dimensional in nature.
It is formed where project actions are listed along
horizontal axis and their environmental impacts in the
vertical axis.
A simple “x” is given to those pairs that have an interaction
between themselves.
TIME DEPENDENT MATRIX
2-dimensional matrix.
Include a number sequence to represent the
time scale (eg.one figure per year) of the
impacts.
 MAGNITUDE MATRIX
Go beyond the mere identification of impact
according to their magnitude, importance
and or time frame(eg short, medium, long
term)
The magnitude of the impact is denoted in
the matrix by putting symbols.
  QUANTIFIED MATRIX
The best known type of quantified matrix is the
Leopold Matrix, which was developed for the US
geological survey by Leopold et al in 1971.
This matrix is based on a horizontal list of 100
project action and a vertical list of 88
environmental components.
 HOW TO USE LEOPOLD MATRIX
 Identify All actions that are part of the proposed project.
 Under each of the proposed actions, place a slash
 at inter section with each item in the side of the
 matrix if an impact is possible.
 HOW TO USE LEOPOLD MATRIX
In the upper left hand corner of each box with a slash,
place a number from 1 to 10 which indicate the
Magnitude of the possible impact; 10 represents- the
greatest magnitude of impact and 1, the least (no
zeroes). Before each number place + (if the impact
would be beneficial).
 In the lower right hand corner of the box place a
number 1 to 10 which indicates the importance of the
possible impact (e.g regional vs local); 10 represents the
greatest importance and 1 the least (non zeroes).
HOW TO USE LEOPOLD
MATRIX
  LEOPOLD MATRIX
The leopold matrix is easily understood, can be
applied to a wide range of developments, and is
reasonably comprehensive for first order, direct
impact.
 LIMITATIONS OF LEOPOLD MATRIX
 It can’t reveal indirect effects of development.
The inclusion of magnitude/significance scores
has additional drawbacks: It gives no indication
on whether these values are based are qualitative
or quantitative.
It doesn’t specify the probability of impact occurring.
                          Advantages
 It presents an easily understood summary of a large number of
    primary impacts.
   It is a generalized but well defined approach, forcing a
    comprehensive consideration of environmental components and
    primary impacts.
   It is an easily performed process which can specify the overall
    character of a project early in the design phase.
   In an extended form, the method can include information about
    many impact attributes, and clarify the assumptions supporting
    the assessments.
   Matrices have low resource requirements.
 WEIGHTED MATRIX
Weighted matrices were developed in an
attempt to respond to some of the above
problems.
Importance weightings are assigned to
environmental components, and sometimes
to project components.
The impact of the project (component) on
the environmental component then
assessed by multiplying the appropriate
weightings with magnitude of impact.
WEIGHTED MATRIX
  OVERLAY METHOD
The overlay approach to impact assessment
involves the use of a series of transparencies to
identify, predict, assign relative significance to, and
communicate impacts in a geographical reference
frame larger in scale than a localized action would
require.
The overlay approach can accommodate both
qualitative and quantitative data.
   OVERLAY METHOD
It   enables   separate     mapping     of    critical
environmental features at the same scale as project's
site plan (Ex: wetlands, steep slopes, soils,
floodplains, bedrock outcrops, wildlife habitats,
vegetative communities, cultural resources, etc).
APPLICATIONS OF OVERLAY METHOD
                The approach has
                been employed for
                selecting highway
                corridors.
                For evaluating
                development options
                in coastal areas.
                Used to map impacts
                spatially and display
                them editorially.
 McHARG OVERLAY
The original overlay technique, the McHarg overlay
is based on a set of transparent maps, each of which
represents the spatial variation of an environmental
parameter (e.g., susceptibility to erosion or
recreational value).
The maps are shaded to show three degrees of
parameter compatibility with the proposed
project.
 McHARG OVERLAY
A composite picture of the overall social cost of
affecting any particular area is approximated by
superimposing all the transparent maps.
  McHARG OVERLAY
Any number of project alternatives can be located
on the final map to investigate the degree of
associated impacts.
The validity of the analysis is related to the type
and number of parameters chosen.
For a readable composite map, the number of
parameters in a transparency overlay is limited
to about 10 (Munn, 1979).
  McHARG OVERLAY
Parameter maps present data in a summarized
and easily interpreted form but are unable to
reflect the possibility of secondary impacts. They
also rely heavily on cartographic skills and their
effectiveness depends to a large degree on
cartographic execution.
 MODERN TECHNIQUE
Modern technique of the same activity is done
using computer software, hardware, data and
skilled people. It is called GIS (Geographic
Information Systems).
The old method is easily adaptable for use with
a computer, programmed to perform the tasks
of aggregating the predicted impacts for each
geographical subdivision and of searching for
the areas least affected.
 MODERN TECHNIQUE
Automated procedures are also available for
selecting sequences of unit areas for routing
highways, pipelines, and other corridors.
The computer method is more flexible, and
has an advantage whenever the reviewer
suggests that the system of weights be
changed.
ADVANTAGES OF OVERLAY
METHOD
It is easy to understand and use.
It has a good display .
It is good for setting site selection.
DISADVANTAGES OF OVERLAY METHOD
 It addresses only direct impacts.
 The burden of ensuring comprehensiveness is largely
 on the analyst
 It does not address impact duration or probability
 The approach is selective because there is a limit to
 the number of transparencies that can be viewed
 together.
 Extreme impacts with small probabilities of
 occurrence are not considered. However, a skilled
 assessor may make indications in a footnote or on a
 supplementary map.
                   Network Method
4
•It uses the matrix approach by extending it take into account
primary as well the secondary impacts.
• Shown in the form of tree called as Relevance/Impact
tree/Sequence diagram.
•Identification of direct, indirect /short and long term environment
impact is a crucial and intact basic step of making Impact tree.
• Used to identify cause-effect linkages
• Visual description of linkages
                 Advantages
•Presentation matrices can only clearly show the primary
or first-order impacts within any particular activity-
component framework. It is possible, however, to
investigate higher order linkages in two dimensions by
using networks.
• It is possible to translate networks into mathematical
models for a more quantitative judgement. The network
method structures the relationships implied in qualitative
simulations.
               Disadvantages:
• One of the main limitations of the network method is
that since impacts are not scored in any quantitative
way, the comparison of project alternatives is not
readily achieved.
• Spatial representation of impacts is not possible.