Title: Integrating Ecological Risk Assessment and Economic Analysis in Watersheds
1Integrating Ecological Risk Assessment and
Economic Analysis in Watersheds
- Randall Bruins
- National Center for Environmental Assessment
- EPA Research and Development
2Topics
- I. Ecological risk assessment and ecosystem
valuation - II. Clinch Valley case study
- Watershed Ecological Risk Assessment
- Economic Analysis
- III. A proposed integration approach
- IV. Ongoing applications
3I. Ecological Risk and Ecosystem Valuation
- Ecological risk reduction
- A key focus of many EPA actions
- A central component of ecological benefits
assessment - Ecological risk assessment (ERA)
- EPAs approach for determining or predicting
risks - Guidelines for Ecological Risk Assessment (1998)
4Watersheds
- Unit for analysis and management
- Five ERA case studies (1993 2000)
- Three economic studies (1999 2003)
5Case Study Goals
- Ecological risk assessment
- Identify key sources, stressors, ecological
endpoints - Characterize risks
- Economic analysis
- Use risk assessment findings
- Conduct decision-relevant analyses
6Economic Case Studies
- Big Darby Creek, Ohio
- O.H. Erekson, O.L. Loucks, Miami University
(Ohio) - Contingent valuation of suburban development
alternatives - Hedonic value (still ongoing)
- Middle Platte River, NE
- R. Supalla, University of Nebraska
- Game theory model of interstate conflict over
water for endangered bird species
7II. Clinch Valley Case Study
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9Watershed Ecological Risk Assessment
- Assessment Team
- U.S. Environmental Protection Agency
- U.S. Fish and Wildlife Service
- The Nature Conservancy
- Tennessee Valley Authority
- U.S. Geological Survey
- Assessment Report
- U.S. EPA (2002). Clinch and Powell Valley
watershed ecological risk assessment. National
Center for Environmental Assessment, Washington,
DC EPA/600/R-01/050. Available at
lthttp//www.epa.gov/nceagt
10Conceptual ModelSources and Stressors
11Conceptual ModelEffects on One Endpoint
12Riparian zone analysis
Fish index of biotic integrity (IBI) at this
sampling point,
Min 500 m
Max 1500 m
100 m
was optimally explained by land cover in
a riparian area of this size
13Risk Characterization
- Up to 55 of stream fauna variability explained
by land uses - Sedimentation, habitat degradation and toxics
most important stressors - Forested riparian areas associated with higher
biological condition - Native fish and mussels are geographically
restricted and highly vulnerable
14Economic Study Team
- University of Tennessee (grantee)
- James Kahn (economist)
- Steven Stewart (economist)
- Oak Ridge National Laboratory
- Robert V. ONeill (ecologist)
- Amy Wolf (anthropologist)
- Held several meetings with ecological risk
assessment team
15Economic Analysis Goal and Rationale
- Goal
- Value biodiversity changes for risk-relevant
management scenarios - Rationale for method
- People lack experience in buying environmental
goods - People do evaluate real-world choices as
alternative attribute-bundles
16Conjoint Analysis Method
- Describes a choice in terms of 3 6 attributes
- Survey presents a series of choice sets in which
attribute levels vary independently - Model estimates each attributes contribution to
probability of a choice - Inclusion of a payment attribute enables WTP
estimates
17Approach
- Define hypothetical policy
- Define ecological, recreational and economic
(i.e., agricultural) attributes affected - Mail survey to sample of valley residents
- Estimate conjoint model
18Choice Attributes
19Sample Choice Set
Please check the option that you would choose
Option A Option B Option C ? ? ?
20Advantage of Conjoint Approach
21Ways to Build Upon This Demonstration
- Clarify the usefulness of welfare estimates in
Clinch Valley management decisions - Quantitatively link the risk and conjoint models
- Estimate impacts of the riparian policies on the
attributes - Make attributes and levels more precise
22III. Proposed Integration Approach
- Interdisciplinary planning and problem
formulation - Decision context determines tools
- Use integrated conceptual models
- Specify management alternatives to allow
interdisciplinary analysis - Quantitatively relate ecological and economic
endpoints
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24Analysis Approaches1. Monetize All Changes
25Analysis Approaches2. Integrate Using Stated
Preference
ANALYSIS CHARACTERIZATION OF ALTERNATIVES
Ecological Risk
Health or Sociocultural
Economics
Quantify endpoint changes where feasible
Quantify endpoint changes where feasible
Quantify financial costs and market-based economi
c effects
Qualitatively describe other changes
Qualitatively describe other changes
Qualitatively analyze equity, economic impact
Express equity effects, impacts in common language
Express primary changes in common language
Express primary changes in common language
Stated preference study
Estimate net social benefits
COMPARISON OF ALTERNATIVES
26Limitations of Clinch Valley Application
27ANALYSIS CHARACTERIZATION OF ALTERNATIVES
Economics
Ecological Risk
Health or Scoiocultural
Quantify endpoint changes where feasible
Create linked model allowing feedbacks
Qualitatively describe other changes
Adjust management alternatives, reiterate
Qualitatively describe all unmodeled changes
Compare quantified and nonquantified endpoint
changes
Compare quantified and nonquantified endpoint
changes
Compare economic equity, impact
COMPARISON OF ALTERNATIVES
28IV. Ongoing Applications
- Integrated conceptual models
- Sources, stressors, ecological endpoints
- Ecosystem services and economic values
- Management alternatives
- National rule application
- Site specific application for water quality
standards (designated use attainment)
29D r a f t
30Watershed Conceptual Model Template
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31D r a f t
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32D r a f t
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