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Modelling of EIAEMS Integration for Proposed Projects

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Title: Modelling of EIAEMS Integration for Proposed Projects


1
Modelling of EIA/EMS Integration for Proposed
Projects
Ph.D. Thesis By Ufuk MALAK, M.Sc.Environmental
Engineer
Supervisor Prof. Dr. Ilhan TALINLI
2
CONTENTS
  • Part 1. Introduction
  • Part 2. Environmental Impact Assessment
  • Part 3. Environmental Management System
  • Part 4. Environmental Risk Assessment
  • Part 5. Modelling
  • Part 6. Model Software
  • Part 7. Results and Conclusion

3
Part 1. Introduction
  • Environment undergoes a continual change
  • Industrialisation (development projects)
    increased environmental degradation.
  • In 1960s, growing environmental awareness has
    focused attention between development actions and
    their environmental consequences
  • Increased awareness of ecological limits to
    industrial growth has stimulated considerable
    interest in developing tools and techniques.

Part 1.Introduction
4
  • Attempts to evaluate the environmental
    consequences of human activities, before such
    activities take place, is an essential part of
    environmental planning and management.
  • Systematic identification and evaluation of
    potential impacts of proposed projects relative
    to physical-chemical, biological, cultural and
    socio-economic components of total environment
    should be made.
  • From that point of view, an assessment tool of
    likelihood impacts was firstly developed in
    Unites States at the beginning of 1970s with the
    name of
  • ENVIRONMENTAL IMPACT ASSESSMENT (EIA).
  • EIA is used as prerequisite for most of proposed
    projects as a Decision Making Process.

Part 1.Introduction
5
  • EIA has found a great application area among the
    countries since 1970.
  • Many evaluation methods are developed and used.
    But towards 1990s, its effectiveness and role in
    sustainable developments are strongly discussed.
  • Monitoring, audit and third party certification
    become important as continuos improvement for
    sustainable development (Rio declaration) become
    very important.
  • 1990s Environmental Management Systems standards
    are developed as a response to various local and
    global environmental problems.
  • Its aim is systematically manage all
    environmental aspects of a facility during
    operational phase.

Part 1.Introduction
6
  • Need to evaluate new methodologies are discussed.
  • Some projects are escaping any kind of assessment
    even they have important impacts. EIA is not
    applicable to all activities but EMS is.
  • It is discussed as best time to introduce an EMS
    is early stages of planning.
  • Cumulative EIA is important by means of time and
    space but traditional EIA does not include it.
  • Also, definition of effected environmental is
    done but no quantitative results are given in EIA
    studies.
  • Most EMS uses the results of EIA and tries to
    systematically manage facility.

Part 1.Introduction
7
  • In this study
  • A determination scale model of EIA and EMS will
    be presented.
  • This model will be determination scale that allow
    of project construction or not.
  • It will give quantitative and repeatable results
    with its new evaluation method.
  • The model will be a feasibility study to
    decision-makers.
  • It will integrate EMS in to EIA studies and
    correspond EMS requirements.
  • Model could be run for alternative processes for
    further decision makings.

Part 1.Introduction
8
Part 2. Environmental Impact Assessment
  • EIA
  • The main purpose of EIA is to inform
    decision-makers of the likely impacts of a
    proposal before a decision is made.
  • is an action forcing mechanism concerned with the
    potential (or real) impacts of proposed (or
    existing) human activities (and their
    alternatives) on the human and natural
    environments.
  • is a planning tool used to predict and evaluate
    the impacts of proposed projects in order to
    assist decision-making.
  • has long been considered an important tool for
    the environmental management of development
    projects.

Part 2. Environmental Impact Assessment
9
  • studies are potentially an important instrument
    for furthering sustainability in public and
    private decision-making
  • should compare alternatives to a proposed project

Part 2. Environmental Impact Assessment
10
EIA History
  • It is first introduction is in U.S. By NEPA in
    1970.
  • It has been applied around the world more than
    30 years.
  • It was appeared in Canada in 1973 (law in 1995),
  • in EU in 1985 and 1997 for member countries
  • In Turkey, first legislation was published in
    1993, than second version in 1997 and two
    additions in 2000.
  • Others are published in very different dates
    (from 1972 until today.

Part 2. Environmental Impact Assessment
11
EIA Process
Part 2. Environmental Impact Assessment
12
EIA Evaluation Methods Checklists
  • Checklists are standard lists and they are one
    dimensional
  • They give an overview of the range of impacts.
  • They do not illustrate interactions between
    effects.
  • Nos statements of likelihood of occurrence are
    being made.
  • Because of subjective nature of estimates, they
    are wont be filled out identically by different
    investigators.

Part 2. Environmental Impact Assessment
13
EIA Evaluation Methods Matrices
  • They are very likely the most popular and widely
    used impact identification methodologies.
  • Leopold matrix (1971) is the most famous one.
  • One-dimensional check lists are expanded to
    two-dimensional matrices.
  • Alternative actions and their impacts can be
    seen.
  • Very often conclusion is stated as a numerical
    value or symbol indicating the level of intensity
    of the effect.

Part 2. Environmental Impact Assessment
14
EIA Evaluation Methods Networks
  • It was developed to consider secondary, tertiary
    and high-order impacts.
  • Developed by Sorensen in 1971.
  • They are mostly used in different land uses as
    tree removal during area preparation and its
    predicted effects as increased surface run-off
    and removal of top soils.

Part 2. Environmental Impact Assessment
15
Major Failures
  • A major failing of EIA practise has been the
    common use of EIA purely to achieve a development
    permit, rather than as a tool to achieve sound
    environmental management within the projects
    objectives of on a broader regional or national
    basis.
  • Its ability to predict impacts and to address
    issues of uncertainty in complex and dynamic
    environmental systems is very difficult.
  • There many questions about its role in decision
    making process
  • It is often considered as a bureaucratic burden.
  • It also considered as time any money consuming
    step.

Part 2. Environmental Impact Assessment
16
Part 3. Environmental Management System
  • EMS provides a mechanism for organisations of any
    size to improve the way they manage environmental
    activities.
  • EMS help an enterprise as
  • Identify and control environmental aspects,
  • achieve its policy, objectives and targets,
  • establish short, medium and long term goals for
    environmental performance,
  • monitoring continual improvement

Part 3. Environmental Management System
17
  • EMS for an enterprise is the systematic
    management of resources and wastes by policies,
    documents, procedures, inventories, monitoring
    and audits.
  • Detailed process survey is required to identify
    all environmental aspects.
  • There are systems standards to implement EMS in a
    enterprise or a facility.

Part 3. Environmental Management System
18
Part 3. Environmental Management System
  • History of EMS
  • British Standards (BS 7750)
  • Eco-Management and Audit Scheme (EMAS)
  • International Standards of Organisations
    Standards (ISO 14000)

Part 3. Environmental Management System
19
BS 7750
  • It is the first EMS standards
  • Published in 1992
  • Reviewed and replace in 1995
  • Became very popular right after its publication

Part 3. Environmental Management System
20
EMAS
  • It is published as regional legislation for UE
    member countries.
  • Firstly adopted in 1993.
  • Replaced BS 7750
  • The revised regulation was published in March
    2001 (provides integration with ISO 14001)

Part 3. Environmental Management System
21
ISO 14000
  • Developed by International Organization for
    Standardization - Strategic Advisory Group on the
    Environment -Technical Committee
  • TC 207 started in 1991
  • Published in September 1996
  • Today most widely used EMS standards in the world
  • Adapted to the other standards as ISO 9000

Part 3. Environmental Management System
22
EMS standards today
Part 3. Environmental Management System
23
Standards ISO 14001
  • It is the most popular and widely used standards
    in the world.
  • Only ISO14001 is the certification part, while
    others documents for EMS.

Part 3. Environmental Management System
24
Part 4 Environmental Risk Assessment
  • It is the most popular and widely used standards
    in the world.
  • Only ISO14001 is the certification part, while
    others documents for EMS.

Part 3. Environmental Management System
25
Relation between, EIA, EMS and ERA
  • EMS mostly uses the results of the EIA (when
    applicable)
  • Best time to introduce an EMS is the EIA phase of
    the process.
  • ERA term sometimes corresponds to EIA.

Part 3. Environmental Management System
26
PART 5 MODEL
Part 3. Environmental Management System
27
Model Approach
  • In this study, integration of EIA and EMS for
    proposed project are modeled.
  • Model are designed to correspond the needs of
    both EIA and EMS.
  • It is though that all required data for the model
    should be given in addition to project designs.
  • Since this is the decision making model, a
    determination scale at the end of the model will
    be evaluated.
  • Model is divided into two parts as state of
    environment part and environmental impacts and
    management parts.

Part 5. Model
28
Model Approach first part of the model
  • All project firstly effect their surroundings
    (near environment)
  • The definition of current state of environment
    should be done.
  • It is possible to allow a project construction
    one some area because of its environmental
    sensitivity, but
  • It may not be possible to allow a project
    construction on another area because of its
    environmental sensitivity.

Part 5. Model
29
Model Approach first part of the model
  • Quantitative definition of effected environment
    with boundaries should be done in each case.
  • That allow as in one region how much project
    construction can be allowed. It gives where to
    stop for new development projects.
  • Changes in state of environment will directly
    give idea about cumulative EIA.

Part 5. Model
30
Model Approach second part of the model
  • Environmental impacts and their management should
    be done at very early stages of the project.
  • As the first part, a permission san be given to
    one project because of its possible environmental
    impacts on a area, some other projects can not be
    allowed to build on the same area.
  • The second part will say how much work will the
    project need to get permission.
  • The second part can easily evaluate the
    alternatives of the project.

Part 5. Model
31
Model Approach
  • Results of the model will be presented in
    values.
  • For the first part, 0 will show the least
    sensitivity while 100 is the most sensitive.
  • For the second part 0 will show the best
    management of impacts while 100 is the worst
    management.
  • The result will be used together as a
    determination scale for decision making.

Part 5. Model
32
Part 1 of the Model State of Environment
  • 5 main categories
  • LAND USE
  • REGIONAL BOUNDARIES
  • ENVIRONMENTAL MEDIA
  • BIOLOGICAL ENVIRONMENT
  • GEOLOGICAL ENVIRONMENT

Part 5. Model
33
Part 1 of the Model State of Environment
Part 5. Model
34
Part 1 of the Model State of Environment
  • Functions and equations
  • EC ? (LU, RB, EM, GE, BE) Equation 1
  • LU ? (PAS, RsD, FA, AgA, TM, IS) Equation 2
  • RB ? (SA, WSPA, NPA, WLPA, WAPA, SEPA, SPA,
    NP, NaP, WL, CH, TR,
    MZ) Equation 3
  • EM ? (WS, AQ, CC, SC) Equation 4
  • GE ? (SGS, NH, UF, MS) Equation 5
  • BE ? (FF) Equation 6

Part 5. Model
35
Equations
  • EC LU RB EM GE BE Equation 7
  • LU PAS RsD FA AgA TM IS Equation 8
  • RB SA WSPA NPA WLPA WAPA SEPA
    SPA NP NaP WL CH
    TR MZ Equation 9
  • EM WS AQ CC SC Equation 10
  • GE SGS NH UF MS Equation 11
  • BE FF
    Equation 12
  • RsD (DsRsA) (PdnRsA) (RMRsA) Equation 13
  • FA AFC DsFA FC Equation 14
  • AgA SC NagAgU Equation 15
  • TM RW WW MW Equation 16
  • IS EP WS WWS Equation 17
  • GW GWQ GWL SP Equation 18
  • GC SGS NH UF MS Equation 19

Part 5. Model Part I
36
Part 1 of the Model State of Environment
  • Results of first part will used the result of the
    second part but
  • It will show the sensitivity of the selected
    area.
  • It will say if the area is available for any kind
    or not by means o threshold value.

Part 5. Model
37
Part 2 of the Model environmental impact and
management
  • WASTEWATER (WW)
  • AIR QUALITY (APM)
  • SOLID WASTE (SWM)
  • HAZARDOUS WASTE (HWM)
  • MEDICAL WASTE MWM)
  • RADIOACTIVE WASTE
  • NOISE POLLUTION (NPM)
  • MANAGEMENT SYSTEM (MS)

Part 5. Model
38
Formulas and equations
  • EIM ? (WWM, APM, SWM, HWM, MWM, RWM, NPM, MS)

Part 5. Model. Part II
39
PART 6. MODEL SOFTWARE
  • A computer program has been developed for the
    model.
  • Programming language of the model is Visual Basic
    Software.
  • Two part of the model will work independently.
  • Results will be presented in values for both
    side of the model.
  • There will be a summary chart warning step for
    important data that user input the model.

Part 6. Model Software
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