+ All Categories
Home > Documents > Methodologies for ecological baselines and prediction...

Methodologies for ecological baselines and prediction...

Date post: 07-Aug-2018
Category:
Upload: duongliem
View: 220 times
Download: 0 times
Share this document with a friend
51
Methodologies for ecological baselines and prediction of impacts on biodiversity resources Dr. Asha Rajvanshi [email protected] Senior Reader and Faculty In-charge, EIA Cell, Wildlife Institute of India, INDIA IAIA ’06 Pre-meeting training course - Stavanger, Norway
Transcript

Methodologies for ecological baselines and prediction of impacts on

biodiversity resources

Dr. Asha Rajvanshi

[email protected]

Senior Reader and Faculty In-charge, EIA Cell,

Wildlife Institute of India, INDIA

IAIA ’06 Pre-meeting training course - Stavanger, Norway

Impact Identification

� Determining what is good and bad about the proposed development ?

Impact is defined as ‘a value

judgment on the importance of a

change measured through varied

parameters and indicators’

Impacts on healthGlobal warming effects Air and water pollution, toxicity Respiratory effects

Impacts on agricultural systemCrop yieldsIrrigation demands

Impacts on forestForest productivity, composition Geographic rangeChange in habitat quality

Impacts on water resourcesChange in water tableChange in water qualityChanges in population of wetland birds

Impacts on coastal areasBeach erosionInundation of coastal land, reduction in coastal habitat

Species and wildlife habitatsLoss of habitat and speciesShift in ecological zones

‘A window into the future’

Impact prediction

� Formal methods standardized as guides/tool kits

� Adhoc methods developed according to the situation

EIA methods

1. Briefing, Consultation and Workshops

2. Checklists

3. Matrices

4. Networks

5. Overlays

6. Other specialized biodiversity or habitat suitability models

7. Computer aided methods

Impact Assessment Procedures

� A variety of methods varying in complexity and characteristics

� All share the common basis of an index of environmental factors or development activities

� Simple checklists

� Descriptive checklists

� Questionnaire checklists

� Weighting-scaling checklists

Checklists

� Provide assessor with a list of factors to be considered, but no information provided on:

Simple checklists

� Used as ‘aide memoir’ to identify impacts

� Can provide structure to initial part of scoping stage

� specific data needs

� methods of assessing importance of impacts

� ways of measuring change to environmental factors

Noise Impacts Construction Phase

I. Noise impacts x

A. Public health

B. Land use

II. Air quality impacts x

A. Public health

B. Land use

III. Water quality impacts x

A. Groundwater

I. Flow and water-table alteration

2. Interaction with surface drainage

B. Surface water

I. Shoreline and bottom alteration

2 Effects of filling and dredging

3. Drainage and flood characteristics

more….

Simple checklists of Potential Impacts of the construction phase of the Transportation Project

Noise Impacts Construction Phase

C. Quality aspects

I. Effect of effluent loadings .

2. Implication of other actions, such as

a. Disturbance of benthic layers

b. Alteration of currents

c. Changes in flow regime

d. Saline intrusion in groundwater

3. Land use

4. Public health

IV. Soil erosion impacts x

A. Economic and land use

B. Pollution and siltation

V. Ecological impacts x

A. Flora

B. Fauna (other than humans)

Wildlife x x x xEndangered Species xNatural Vegetation x x xExotic Vegetation xGrading x x x xSoil Characteristics x x xNatural Drainage xForest Productivity x x x xNoise x xSurface Paving xRecreation x x xAir Quality x xxVisual Disruption xOpen Space x x x xHealth and Safety x x x xEconomic Values x x xPublic Facilities x x x x(Including schools)Public Services x x xConfirmity to Regional Plans x x x

No Effects

Positive effect

Negative effect

Beneficial

Adverse

Problematic

Short-term

Long-term

Reversible

Irreversible

Environmental Areas

Descriptive checklist

Limitations – It only recognises impact - ? Quantitative information - nil

� Will the project lead to impacts on herbivores species

Yes No Not known

� Will the project involve submergence of critical habitats of endangered species

� Will the project lead to acid mine drainage into a wetlands

� Will the removal of some tree species during forest clearance for reservoir significantly effect the fodder resources for elephants

Part of a questionnaire checklist

Yes No Not known

Yes No Not known

� Comparatively simple method

� Not necessarily project specific

� Once established, can be used in many different situations

Benefits of checklists

� It only recognises impact and provides no quantitative information

� Can never be considered as definite or complete

� Do not help to identify secondary/higher order impacts

� Tend to compartmentalise

Problems with checklists

� Two dimensional version of a checklist

� Attempts to identify interactions between development actions on one axis and environmental parameters on the other

� Variety of forms available

Interaction matrices

� Developed by United States Geological Survey 1971

� 100 actions x 88 environmental items

� IMPACT - identified at the interaction between the above

� Impacts can be identified:

Leopold matrix

� by signs: ���� ���� ���� ���� ����

� qualitatively: ‘good’, ‘moderate’, ‘high’

� quantitatively: absolute/relative (NOT OBJECTIVE)

� Impacts can be POSITIVE or NEGATIVE

MI

Actions causing impactEnvironmental items

Magnitude

Leopold interaction matrix

meaning of x/y: x = Relative magnitudey = Relative importance

a,b,c, are activities

A,B,Care environmental parameters

Leopold matrix

etc.

2/24/67/24/52/3D

3/61/15/59/78/87/2C

3/34/94/81/10B

3/78/52/1A

etc.gfedcba

Part 1 : Project Actions

A. Modification of Regime

a) Exotic flora or fauna introduction

b) Biological controls

c) Modification of habitat

d) Alternation of ground cover

e) Alternation of ground-water hydrology

f) Alternation of drainage

g) River control and flow codification

h) Canalization

i) Irrigation

j) Weather modification

k) Burning

l) Surface or paving

m) Noise and vibration

B. Land transformation and constructiona) Urbanizationb) Industrial sites and buildingsc) Airportsd) Highways and bridgese) Roads and trailsf) Railroadsg) Cables and liftsh) Transmission lines, pipelines, and

corridorsi) Barriers, including fencingj) Channel dredging and straighteningk) Channel revetmentsl) Canalsm) Dams and impoundmentsn) Piers, seawalls, marinas & sea terminalso) Offshore structuresp) Recreational structuresq) Blasting and drillingr) Cut and fills) Tunnels and underground structures

The Leopold Matrix (Leopold et al., 1971). Part 1 Lists the Project Actions (Arranged Horizontally in the Matrix); Part 2 Lists the Environmental ‘Characteristics’ and ‘Conditions’ (Arranged Vertically in the Matrix)

C. Resource Extraction

a) Blasting and drilling

b) Surface excavation

c) Sub-surface excavation and retorting

d) Well drilling and fluid removal

e) Dredging

f) Clear cutting and other lumbering

g) Commercial fishing and hunting

D. Processinga) Farmingb) Ranching and grazingc) Food lotsd) Dairyinge) Energy generationf) Mineral processingg) Metallurgical industryh) Chemical industryi) Textile industryj) Automobile and aircraftk) Oil refiningl) Foodm) Lumberingn) Pulp and papero) Product storage

E. Land Alteration

a) Erosion control and terracing

b) Mine sealing and waste control

c) Strip mining rehabilitation

d) Landscaping

e) Harbour dredging

f) Marsh fill and drainage

F. Resource Renewal

a) Reforestation

b) Wildlife stocking and management

c) Ground-water recharge

d) Fertilization application

e) Waste recycling

G. Changes in Traffic

a) Railway

b) Automobile

c) Trucking

d) Shipping

e) Aircraft

f) River and canal traffic

g) Pleasure boating

h) Trails

i) Cables and lifts

j) Communication

k) Pipeline

H. Waste Emplacement and Treatment

a) Ocean dumping

b) Landfill

c) Emplacement of tailings, spoil, and overburden

d) Underground storage

e) Junk disposal

f) Oil-well flooding

g) Deep-well emplacement

h) Cooling-water discharge

i) Municipal waste discharge including spray irrigation

j) Liquid effluent discharge

k) Stabilization and oxidation ponds

l) Septic tanks, commercial & domestic

m) Stack and exhaust emission

n) Spent lubricants

I. Chemical Treatment

a) Fertilization

b) Chemical deicing of highways, etc.

c) Chemical stabilization of soil

d) Weed control

e) Insect control (pesticides)

J. Accidents

a) Explosions

b) Spills and leaks

c) Operational failure

Others

a)

b)

Leopold matrix

Matrices

� Magnitude matrix

� Time dependent matrix

� Weighted matrix

Advantages of matrices

� Easily modified, so many varieties have been developed and used

� Relationships between development and environment made explicit

� Can present a summary of anticipated impacts in an easily understood format

� Can also be useful in scoping

Suggested matrix for impact determination

Disadvantages of matrices

� Fail to identify potential secondary or tertiary impacts

� May not provide an objective method for comparing impact magnitudes or importance

Networks

� Means of establishing the causal chain of impacts

� Offers a three dimensional approach to identifying impacts

� Can be limited by minimal information on technical aspects

� Can be visually complicated

Project ActivitiesPrimary Secondary Tertiary

Components of Activities

Impacts

Conceptual model of impact

networks.

Networks – High order linkages between causes and effects

Causal fa

cto

rs

Sew

age s

yste

m

Macadam

ized s

urf

aces

Excavation

Tre

e r

em

oval

Uses High-

density

apartments

Play areas

Parking areas

Removal of

topsoil

Pollution of

ground-water

Increased

surface runoff

Initial

conditions

Decreased

fertility

Degradation of

water-supply

Flooding

Death

of flora

Health

hazard

Gullying

+ erosion

Possible adverse impacts

Consequent

conditions

Third

order

effects

Landscape

gardening

Planting of

shrubs

Building

code

Corrective

actionsControl

mechanisms

A portion of Sorenson’s network used to display the possible consequences of various forms of land use (Sorenson, 1971)

Major land use type Residential

Identifies direct and indirect impacts

Deforestation & Loss of Biodiversity

Selective Cutting of trees for

Curio Wood

Demand for

Curios Increased

Erosion of Gorge

Access Paths

More Rafting

Licenses

River Bank Erosion

Water

Pollution

Wave

Effects

Riparian Vegetation

Reduced

River Bank & Island

Development

More Jetties &

Boat Licenses

Overgrazing Around

Water Holes

Loss of Habitat

CHANGING QUALITY OF LIFE FOR WILDLIFE

Oily discharges

from boats etc.

Increased Incidents

between Wildlife & People

Changes in

Animal Behaviour

Too small an area for animal numbers

Constriction of wildlife

movements

More Fences/

Enclosures

Expansion of Hotels/Camps

& Tourist Facilities

Increased Visitor Numbers

Visual

Impacts

Loss of Natural

Wilderness Value

Harassment

of wildlife

Disturbance of wildlife

Increasing noise levels

More Aircraft Flying Over

Falls & Town

More

Motor Vehicles

New Road & Bridge

CHANGING QUALITY OF TOURISM

Demand for Low-spending

Tourism Increases

More Direct

International Flights

Airport Upgrading

Improved Border

Facilities

Increased customs co-operation

Improved Road Links

Source: UNEP, 2002

Fisheries Water quality

Fish

Aquatic

macrophyte

Dissolved

oxygenAlgae

Nitrogen and phosphorus

concentration in water

Vegetation

buffer

Soil

Reduction in

fertilizer application

Application of

inorganic fertilizer

Network diagram of the causal chain that begins with application of inorganic fertilizers

Composite

Ecological sites

Historic sites

Visual

Health

Settlements

Noise

Severance

Water

Overlays

Advantages: Easy to understand, good display method and good siting tool

Disadvantages: Address only direct impact,

Schematic representation of Map Overlay procedures that enable delineation of most preferred road alignment (Route A) option to avoid sensitive habitats (core area of Tiger Reserve shown in grey scale) and sites of animal distribution (represented by dots)

Benefits of overlays

� Conceptually simple

� Provide clear presentation

� Highly versatile

� Appropriate for assessing impacts occurring on large areas (impacts of hydropower project on regional hydrology, landscape level impacts)

� Can predict geographical location of impacts

� Very useful in developing site for alternatives

Limitations

� Setting boundaries of certain parameters is difficult leading to distorted information

0 102 4 6 8

NET IMPACT

Predicted Condition

Without Project

Predicted Condition With

Project10

20

30

40

50

60

70

80

90

100

Target Years

Habitat U

nits

Habitat Suitability Index Models

Methods of analysis of impacts

� Professional judgement

� Quantitative mathematical models

� Experiments, indices and models

� Case studies

Soundness of predictions based on professional judgement

� Emission of gases from stacks were expected to have deleterious

effects on plant life

� The impact on the aquatic system was expected to be small

� The water fluctuation resulting from the project may seriously

affect nesting and feeding grounds of water birds

� Amphibians and reptiles inhabiting wetland areas would be

adversely affected by Narmada Project

� Terrestrial fauna were expected to be negatively affected

through direct loss of habitat to submergence

� Pipeline along the Great Indian Bustard habitat will have serious

impact on GIB breeding

Determine impact significance

� Evolve criteria for assessing impact characteristics

Criteria for identifying impact significance

� Duration of project related actions

� Location of project site

� Urgency and quickness with which the natural systems might deteriorate

� Degree of irreversible damage to natural resource base and resource quality

Ecological significance criteria

� Reduction in species

� Habitat depletion or fragmentation

� Threatened, rare and endangered species

� Impairment of ecological function� Disruption of food chain

� Decline in species population

� Alteration in predator-prey relationship

Determination of significance of negative impacts

Developing a matrix using importance value criteria for determining conservation value of habitats and species

Scaling impact assessment

Adding dimensions to impacts

631435Total score

100011Mammals (Dolphin)

110110Migratory Birds

100001Crocodiles

110101Turtles

211212Fishes

GangesHaroharKiulAjoyDamodarRupnarayan

Major riversAquatic fauna

Score:Fish: 1=<5 Spp.; 2=6 – 10 Spp.; 3 =>10 Spp. Turtle: 0=Absent, 1=Present

Migratory: 0=Absent, 1=Presentwater fowl

Aquatic : 0=Absent, 1=Presentmammals

Scoring for wildlife values

27611311124163225Total

2

5

5

5

10

2

1

1

1

1

1

5

0

5*

0

1

1

0

1

0

1

0

0

0

0

1

0

0

0

0

2

5

0

5

0

2

1

0

1

0

1

0

0

5

10

1

0

0

1

1

2

5

5

0

10

2

1

1

0

1

0

5

5

5

10

Fishes

Turtles

Crocodiles

Migratory waterfowl

Aquatic mammal (Dolphin)

Wild-life value with CSF

Wild-life value score

Wild-life value with CSF

Wild-life value score

Wild-life value with CSF

Wild-life value score

Wild-life value with CSF

Wild-life value score

Wild-life value with CSF

Wild-life value score

Wild-life value with CSF

Wild-life value score

GangesHaroharKiulAjoyDamodarRupnarayanCSF values

Faunal groups

* Baer's pochard sighting

Scale for conservation significance

Dimensions of disturbances

Dimensions of impact

Impact prediction is ultimately dependent on

� Probability of risk

� Predictability of an event or a trend

Predicting impacts on biodiversity is difficult but not impossible!


Recommended