setting the context: ecosystem service analysis · 2017-04-10 · setting the context: ecosystem...
TRANSCRIPT
Setting the Context: Ecosystem Service Analysis
Lisa A. Wainger
University of Maryland Center for Environmental Science
STAC workshop on Ecosystem Goods and Services
3/28/17
Total Economic
Value
Use Value
Direct Use
- I’m enjoying nature
Indirect Use
- Nature does thatfor me?!
Option
- I might need it
later
Non Use Value
Existence
- I just like it
Bequest
- I want my grandkids to
enjoy it
Altruistic
- I want to help others who might
need it
Increasing difficulty of valuation ($)
Economic Value = Anything that contributes to human well-being
Non-use values can be substantial (from Wainger, Secor et al., in press)
Ecosystem service Spatial extent of beneficiaries
Monetary valuesfor TMDL
Authors
Property value enhancements due to enhanced water clarity
Waterfront & near-waterfront homes
$400-$700 million (present value)
Klemick et al. (2016)
Property value enhancements due to expanded SAV extent
Waterfront & near-waterfront homes
$300-$400 million Guignet et al. (2016)
Multiple use and non-use benefits [changes in abundance of striped bass, crab and oysters, water clarity in the bay, and algae in lakes]
About 80% of the total benefits accrued to non-users of the Bay
$1.20 to $6.49 billion / year
Moore et al. (2015)
Climate change damage costs avoided (carbon sequestration)*
Watershed $12.6 million/year US EPA (2011, Scenario 8a)
Health and aesthetic benefits due to air quality improvements*
Watershed $2.5 million/year US EPA (2011, Scenario 8a)
Hunting* Watershed $0.2 million/year US EPA (2011, Scenario 8a)*Optimized scenarios - not WIPs
Valuation does not measure overall importance• Builds social preferences from individual preferences
• People get to choose what they like
• What people will pay is determined by supply and demand conditions
• Benefits to society are measured as the aggregate of what everyone prefers
• Does not address • Fairness
• Distribution of benefits and losses among stakeholders
• Biases or information gaps that may prevent people from making optimal choices
Values Are Not Market PricesPrice of Carbon Credit
Based on supply & demandconditions
Based on benefitsto society (avoided damage toproperty, crops,health, etc.)
Values Are Rarely Potential Income
Because values are not market prices -
• Benefits do not represent money you could receive in transactions
• What can be valued might not be what motivates someone to act• Same management practice might improve soil health & sequester carbon
• Relatively easy to value carbon sequestration
• But farmer may be more motivated to adopt by changes in soil health
Values Are for Small Changes, Not the Whole Enchilada• Economists can only value small-moderate size changes in services
• People adapt and substitute when there are large changes
• Costanza approach of valuing the worlds ecosystems has been called “a serious underestimate of infinity”, Why?• A: Value changes as services become scarcer
• Values based on a per-acre value are better thought of as “promotional values”
Ecosystem service values tailored to location promote cost-effective planning
Cost-effectiveness of manure transportation subsidiesRed areas: Combined benefits for subsidizing manure transport are projected to be the highest per dollar spent (white areas = missing data)
Benefit index includes 1) Opportunity to reduce nutrient runoff from manure 2) Likelihood of nutrients reaching a stream3) Potential to improve impaired local water quality or protect areas with high habitat quality or high demand for fishing
Magen and Wainger, 2016
Economic Impacts are a Local Benefit
• Any money spent generates jobs and economic activity
• Jobs created depends on structure of local economy, not the social importance of the investment
Model of economic structure
• Direct effects • Indirect effects • Induced effects
Spend money
JobsEconomic Activity
How do we value ecosystem services to promote sound decisions?
Conceptual Value Diagram
ActionEcological outcome
Benefit-Relevant
Indicators
Who cares?
Social Benefits
How much do they care?
Alternative Benefit Measures with Increasing Economic Content
Ecological Outcome Metrics
Benefit Relevant Indicators
Social Benefits
% change game fish Likely # anglers Willingness to pay
Figures from Mazzotta, Wainger, et al. 2015
Act
ion
Practical & feasible methods for measuring values
One example
Reductions in nutrient and
sediment inputs
Reduced risk of climate change
Benefits to Stakeholders
Ecosystem Service Indicators
Flood and drought mitigation
Improved recreational
opportunities and aesthetics
Waterfowl habitat*
Wastewater treatment plants
Stormwater detention ponds
Septic upgrades
Gray options
Wetland restoration
Reforestation
Riparian buffers
Green options
Water storage*
GHG mitigation*
Hunting, fishing and birding
Freshwater fish habitat*
* Bonus Ecosystem ServicesBioretention
Animal habitat*
Gray vs. Green Options and the Provision of Ecosystem Service Co-Benefits
Weighting ecological changes by potential for benefits
US EPA 2011
Flood protection value highest when BMP is upstream of urban area + downstream of flood control dams
Using economic benefit transfer
Table 3-15. Annual Values* of Pollutant Removal by Urban Stormwater BMPs ($/acre of BMP/year)
US EPA 2011
* Health + other benefits accrue in urban areas with air quality problems
Using Ecosystem Services Values to Compare Implementation Choices
$0
$10
$20
$30
$40
$50
$60
Base CaseLC
RestrictedNPS LC
Base CaseLNC
RestrictedNPS LNC
$M
illio
nAir Quality
Duck Hunting
Non-WaterfowlHunting
Carbon Sequestration& Reduced GHGEmissions
Max BenefitsLeast Cost
US EPA 2011
Using both monetized and non-monetized benefits provides a balanced picture of benefits
0
5
10
15
20
25
30
35
40Ec
on
om
ic B
enef
it In
dex
Non-MonetizedBenefitsMonetizedBenefits
urban
- Property protection- Recreation
rural
- Existence- Bequest
18
Values that support good decisions
• Reflect ecological effectiveness of management practices
• Include location characteristics that determine if service is possible & needed
• Reflect peoples’ degree of concern for the change
• Include use and non-use values to represent a broad portfolio of ecosystem service benefits
References• Klemick, H., C. Griffiths, D. Guignet, and P. Walsh. 2016. Improving Water Quality in an Iconic Estuary: An Internal Meta-
analysis of Property Value Impacts Around the Chesapeake Bay. Environmental and Resource Economics:1–28.
• Guignet, D., C. Griffiths, H. Klemick, and P. J. Walsh. 2016. The Implicit Price of Aquatic Grasses. Marine Resource Economics 32:21–41.
• Mazzotta, M., L. Wainger, S. Sifleet, J. T. Petty, and B. Rashleigh. 2015. Benefit transfer with limited data: An application to recreational fishing losses from surface mining. Ecological Economics 119:384–398.
• Moore, C., D. Guignet, K. B. Maguire, C. Dockins, and N. B. Simon. 2015. A Stated Preference Study of the Chesapeake Bay and Watershed Lakes. National Center for Environmental Economics, US Environmental Protection Agency.
• US EPA. 2011. An Optimization Approach to Evaluate the Role of Ecosystem Services in Chesapeake Bay Restoration Strategies. Office of Research and Development. US EPA/600/R-11/001
• Wainger LA, Secor D, Gurbisz C, Kemp M, Glibert PM, Richkus J, Barber M. (in press). Resilience indicators support valuation of estuarine ecosystem restoration under climate change. Ecosystem Health and Sustainability.
• Wainger, L. A., G. Van Houtven, R. Loomis, J. Messer, R. Beach, and M. Deerhake. 2013. Tradeoffs among Ecosystem Services, Performance Certainty, and Cost-efficiency in Implementation of the Chesapeake Bay Total Maximum Daily Load. Agricultural and Resource Economics Review 42:196–224.
• Wainger, L. A., R. J. Johnston, K. J. Bagstad, C. F. Casey, and T. Vegh. 2014. Social Impact Analysis: Monetary Valuation. In: The Federal Resource Management and Ecosystem Services Guidebook (Olander, L. et al. eds.). National Ecosystem Services Partnership, Nicholas School of the Environment, Duke University. https://nespguidebook.com/assessment-framework/monetary-valuation.