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Developing Ecosystem Services Science for Policy Developing Ecosystem Services Science for Policy Needs in the Willamette Basin, Oregon, USA:Needs in the Willamette Basin, Oregon, USA:
A Place-Based StudyA Place-Based Study
Linking Human Well-Being with Ecosystem Services
ACES Meeting – Naples, FL 09 Dec 2008
Dixon H. Landers, Robert McKane, Jana ComptonRene Brooks, Paul Rygiewicz, John Bolte and ConnieBurdick. USEPA, Western Ecology DivisionCorvallis, OR USA
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The EPA Challenge:The EPA Challenge:
Change the economic and human Change the economic and human well-being foundation for well-being foundation for
environmental decision-makingenvironmental decision-making
Current Investment:
200 Scientists
~$62 million dollars supporting research
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Ecological Services Research Program Ecological Services Research Program Goals:Goals:
Long-Term Goal 1: National policy makers will have the tools Long-Term Goal 1: National policy makers will have the tools and technologies to develop scientifically-defensible and technologies to develop scientifically-defensible assessments of the state of our nation’s ecosystems and the assessments of the state of our nation’s ecosystems and the effectiveness of existing national programs and policieseffectiveness of existing national programs and policies
Long-Term Goal2: States and tribes apply improved tools and Long-Term Goal2: States and tribes apply improved tools and methods to protect and restore their valued ecological methods to protect and restore their valued ecological resourcesresources
Long-Term Goal 3: Decision-makers understand the Long-Term Goal 3: Decision-makers understand the importance of ecosystem services and make informed, importance of ecosystem services and make informed, proactive management decisions that consider a range of proactive management decisions that consider a range of alternative outcomesalternative outcomes
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UsesUses Setting policies and guidelines:Setting policies and guidelines:
• EPA often seeks to promote its mission through a variety of policy instruments that do not have the legal force of national rules. .
Quantifying benefits for national rule-making: Quantifying benefits for national rule-making: • The Office of Management and Budget establishes data requirements
needed to assess the benefits and costs associated with these rules. Developing environmental GDP accounts or other Developing environmental GDP accounts or other
environmental indicators: environmental indicators: • In recent years, there have been numerous calls for establishing
environmental accounts within our national Gross Domestic Product accounts.
Acting as a catalyst for market innovations: Acting as a catalyst for market innovations: • In some cases, EPA seeks to engage the private sector directly in its
efforts to improve environmental conditions.
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EPA Ecological Services Research EPA Ecological Services Research Program - Place-Based StudiesProgram - Place-Based Studies
Southwest
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Why Place-Based Research?Why Place-Based Research?
Work with actual, interested end-point users of research Work with actual, interested end-point users of research tools to assist with design and implementationtools to assist with design and implementation
Confront contextual social and economic forces, Confront contextual social and economic forces, challenges and solutionschallenges and solutions
Test models with appropriate data types and coveragesTest models with appropriate data types and coverages Develop a manageable approach to scalingDevelop a manageable approach to scaling Enlist “local” experts with knowledge tailored to the Enlist “local” experts with knowledge tailored to the
question and issuesquestion and issues Compare Compare likelike and contrast and contrast differentdifferent approaches to approaches to
similar issues among PBPssimilar issues among PBPs Synthesize knowledge derived from the above activities Synthesize knowledge derived from the above activities
to determine what level of information is ADEQUATE for to determine what level of information is ADEQUATE for decision makers to project ES at a national scale.decision makers to project ES at a national scale.
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Willamette Basin:Willamette Basin:
A Place Based StudyA Place Based Study
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Willamette Ecosystem Willamette Ecosystem Service District Service District
65% Forest65% Forest 20% Ag; 11% Urban20% Ag; 11% Urban 4% Riparian Wetland4% Riparian Wetland Not all forests are equalNot all forests are equal
• High elevation (N sensitive or N retentive?)• Broadleaf vs. Conifer
Portland, OR
LandcoverLandcover
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Why the Willamette? Why the Willamette?
Willamette “Ecosystem Service District” provides a broad range of Land-Willamette “Ecosystem Service District” provides a broad range of Land-Use/Land-Cover, stressors, gradients, and diverse, linked settingsUse/Land-Cover, stressors, gradients, and diverse, linked settings
WED Alternative Futures research experience (mid 1990’s) = rich data sets, WED Alternative Futures research experience (mid 1990’s) = rich data sets, experienced researchers, potential collaborators (NRCS, USACE, USDA-experienced researchers, potential collaborators (NRCS, USACE, USDA-FS, USGS, OWOW, etc.) FS, USGS, OWOW, etc.)
Well Connected Research and Regulatory Entities now Working toward Well Connected Research and Regulatory Entities now Working toward future Ecosystem Service trading (Region X)future Ecosystem Service trading (Region X)
Multiple related Star Grant recipients (OSU, OU, PSU)Multiple related Star Grant recipients (OSU, OU, PSU) Willamette Partnership (State Non-Profit); OWEBWillamette Partnership (State Non-Profit); OWEB Trading Scenario for Temperature (riparian wetland ecosystem service) Trading Scenario for Temperature (riparian wetland ecosystem service)
rapidly developing – EPA Funding with Region X oversightrapidly developing – EPA Funding with Region X oversight ORD Multi-Year Plan – Ecosystem Research Program: provides explicit ORD Multi-Year Plan – Ecosystem Research Program: provides explicit
context context
CLIMATE OF OPPORTUNITY
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Overall Goal:Overall Goal:The W-ESP seeks to provide a scientifically based decision support system for The W-ESP seeks to provide a scientifically based decision support system for valuing and projecting ecological services resulting from alternative management valuing and projecting ecological services resulting from alternative management decisionsdecisions
Objectives:
Quantify ecosystem services, including their distribution and status.
Provide models to predict responses of ecosystem services to probable future conditions.
Identify critical knowledge gaps in our understanding of how ecosystem services are provided.
Evaluate net benefits of bundled ecosystem services and tradeoffs among management actions that affect these services.
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Translating services into quantifiable spatial metrics
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Avoiding Unintended Consequences
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Willamette Conceptual Model: ALL LAND USES
$ $ $ $ $ Non-Economic Value Stakeholder Prioritization
Sediment Regulation
Water Quantity
Water Quality
Carbon Sequestration
Ag & Forest Products
Fire Regulation
Fish & Wildlife
ExtractiveEnergy, Minerals, Rx
RecreationSense of
PlaceAir QualityBiodiversity
GHG Regulation
STRUCTURESpecies, Food Webs,
Spatial Organization, Soils
Terrestrial Ecosystem Aquatic Ecosystem
FUNCTIONCarbon, Nutrient & Water Cycling;
Soil Formation & Degradation, Competition, Reproduction, Mortality, etc
STRUCTURESpecies, Food Webs,
Spatial Organization, Benthic & Water Column
FUNCTIONCarbon, Nutrient & Water Cycling;
Sediment Dynamics, Groundwater InteractionsCompetition, Reproduction, Mortality, etc
Agricultural Land Use
Forest Land Use
Riparian Land Use
Water Quality & Quantity
GCC Mitigation
Fish & Wildlife
Energy & Minerals Wilderness
Recreation & Tourism
GlobalChange
ChemicalsLand, Air, Water
WaterUse
Land Cover
Environmental Stressors / Drivers Anthropogenic Stressors / Drivers
Land Use
ClimateSoils & Hydro-geomorphology Fire Hunting &
FishingOther
ExtractivePests & invasives
ΔΔ Stressors / Stressors /DriversDrivers
ΔΔ Stressors / Stressors /DriversDrivers
ΔΔ Ecosystem Ecosystem(Quantitative ERFs)*(Quantitative ERFs)*ΔΔ Ecosystem Ecosystem
(Quantitative ERFs)*(Quantitative ERFs)*
ΔΔ Ecosystem EcosystemServicesServices
(Quantitative EPFs)**(Quantitative EPFs)**
ΔΔ Ecosystem EcosystemServicesServices
(Quantitative EPFs)**(Quantitative EPFs)**
ΔΔ Value Value (of ES Bundle)*** (of ES Bundle)***
ΔΔ Value Value (of ES Bundle)*** (of ES Bundle)***
Ada
ptiv
e M
anag
em
ent
ΔΔ Human HumanWell-being***Well-being***
ΔΔ Human HumanWell-being***Well-being***
DecisionsDecisionsPolicy, Regulatory, Policy, Regulatory,
Economic, Political…Economic, Political…
DecisionsDecisionsPolicy, Regulatory, Policy, Regulatory,
Economic, Political…Economic, Political…
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Inventory of Current Ecosystem Services: Inventory of Current Ecosystem Services: Approach and Knowledge Gaps Approach and Knowledge Gaps
1.1. Identify key ecosystem services (ES) Willamette Identify key ecosystem services (ES) Willamette Ecosystem Services DistrictEcosystem Services District
2.2. Determine appropriate units for ESDetermine appropriate units for ES
3.3. Develop an approach to inventory, “scale” and map ESDevelop an approach to inventory, “scale” and map ES
4.4. Identify knowledge gaps in assessing ESIdentify knowledge gaps in assessing ES
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EffectsEffects
Cross Place Based Coordination on ESCross Place Based Coordination on ES
Models
Wildlife Populations
Plant Communities
Biogeochemistry
Hydrology
StressorsStressors
Stressors Land Use
• Forest• Agriculture• Riparian • Urban
Global Change• Climate• CO2
• N deposition Chemicals
• Fertilizers• Pesticides
Terrestrial Services Ag products Forest products C sequestration Nutrient regulation GHG regulation Habitat quality Wildlife populations
Aquatic Services Water quality Water quantity Fish & waterfowl
NutrientCycling
Productivity
Biodiversity
WaterQuantity
WaterQuality
CarbonStorage
Sense ofPlace
?? Social Scientist ??
WillametteESRP-Wide “Common” Services
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Forcing Variables (Stressors)Forcing Variables (Stressors) Natural and anthropogenic factors affecting quantifiable changes in
the status (e.g. amounts & fluxes) of ecosystem processes
ERF: Ecological Response FunctionERF: Ecological Response Function The response of an ecosystem service to a particular forcing variable
ETF: Ecological Trade-off FunctionETF: Ecological Trade-off Function The relationships between two (or more) ecosystem services in
response to the same forcing variable (…and, eventually, multiple forcing variables)
Definition of Terms Used to Determine Definition of Terms Used to Determine Future Responses of Ecosystem Services toFuture Responses of Ecosystem Services to
Multiple Response VariablesMultiple Response Variables
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Socioeconomics
Valuation & Trading of Ecosystem Services
ERF Y-axis: Ecosystem Services• Food/fiber Yield• Carbon Sequestration • Water Quality• Water Quantity• GHG regulation (N2O, NOx, CH4 …)
ERF X-axis: Forcing Variables• Soils & Geology• Climate (Temp, Precip, Light, CO2)• Fertilization Practices• Tillage Practices• Cover Type (Species, Riparian Buffers…)• Many others…
ERF1 + ERF2
Tradeoff = ETF
N Fertilization
N E
xpor
tYield
N Export
Cro
p Y
ield
N Fertilization
Cro
p Y
ield
ERF1
Ecosystem Service vs. Forcing Variable = ERF
N Fertilization
N E
xpor
t
ERF2
Conceptual FrameworkConceptual Framework
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FertilizationFertilization
TillageTillage
Drought Index Drought Index
Str
eam
Nit
rate
Drought Index
ClimateClimate
Cro
p Y
ield
Soi
l Car
bon
Water Water QualityQuality
CarbonCarbonSequestrationSequestration
Food Food ProductionProduction
Str
eam
Nit
rate
N FertilizationN Fertilization
Cro
p Y
ield
Str
eam
Nit
rate
Tillage
N Fertilization
Soi
l Car
bon
Soi
l Car
bon
Tillage
Cro
p Y
ield
Tillage
Some Agricultural ERFs & ETFsSome Agricultural ERFs & ETFs• Read vertically to compare responses (ERFs) for a given service to 3 different stressorsRead vertically to compare responses (ERFs) for a given service to 3 different stressors
• Read horizontally to assess trade-offs (ETFs) among 3 services at any given stressor levelRead horizontally to assess trade-offs (ETFs) among 3 services at any given stressor level
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Models: Statistical and Process-BasedModels: Statistical and Process-Based
Synthesize & Scale Up Data Plots to Region, Days to Centuries
Plots, Stands Hillslopes, Catchments Basin, Regionsnobear.colorado.edu/IntroHydro/hydro.gif
Scaling Up Ecosystem Services – Using Biophyical ModelsScaling Up Ecosystem Services – Using Biophyical Models
N Fertilization
Cro
p Y
ield
Plot-Scale ERFs
Buffer Width
N E
xpor
t
Hillslope-Scale ERFs
Ag:Forest Area Ratio
N E
xpor
t
Basin-Scale ERFs
More Buffers
Deep flowpaths
Shallow flowpaths
Low % sand Less Buffers
??High % sand
?
Using nitrogen addition & export as an example…
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Issues of ScaleIssues of Scale
1. Spatial Extrapolation1. Spatial Extrapolation
Known Known
2. Decision Making and the 2. Decision Making and the Adequacy Adequacy of of Scientific UnderstandingScientific Understanding
e.g. Region to Tax Lote.g. Region to Tax Lot
Unknown
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Inventory and mapping the location and value of Ecosystem Services is an essential activity of W-ESP
W-ESP (Chan et al. 2006)
Develop an Develop an approach to approach to inventory inventory and map ESand map ES
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Modified from John Bolte, Oregon State University
Quantification and Valuation of Ecosystem
Services: apply indicators
reflecting quantityLandscape:
Spatial domain in which land
use changes and other
stressors are depicted Natural Change
Processes: Models of non-human change
Actions
Policies: Constraints and actions defining
land use management
decisionmaking
PolicySelection
Clients: making multiple decisions
by selecting policies
responsive to their objectives
Landscape Feedback
Decision Support System – General StructureDecision Support System – General Structure
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Hypothetical ecosystem service values:Bundled by land use in the Willamette ESD
*Relative value could be a rate, say kg/ha/yr, or represent economic or social value.
Rel
ativ
e va
lue*
0
ForestNative
GrasslandHeadwater
WetlandRiparian
forestVegetated
bufferRip Rap
slopeRow crop
Grass seed Urban
Nutrient removal
Temperature regulation
Carbon Sequestration
Habitat
Flood protection
Food & Goods
Ecosystem Services
+
-
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Limitations Regarding ImplementationLimitations Regarding Implementation
Disciplinary Needs:Disciplinary Needs:
Sociologist – Human Health and Well Being; Mediated ModelingSociologist – Human Health and Well Being; Mediated ModelingEconomist – Market and Non-Market ValuationEconomist – Market and Non-Market ValuationModelers – System Approaches and Scaling Modelers – System Approaches and Scaling
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End Product
Scaling and Aggregation
Under Alternative
Management ScenariosVegetated
buffer strip
Forest
Row crop
Livestock
SAV
Mangrove Wetland
Headwaterwetland
Rip Rap slope
Urban
Net Value of Services
Relative Ecosystem ServicesWithin an Ecosystem District
ManagementOption X
A B
C
Options
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Futures & Trading Analyses
Natural & Anthro- pogenic
Stressors
Past,Present
&Future
Riparian wetland ES
C-Sequestration
N-control
Critical habitat
Societal Response&
EPA Policy Actions
Place-Based Societal Issues & Values
Tradable EcosystemService Units
•Predicted climate change•Air pollution•Land use management•Population growth
Forcing Variables:Desired Outcomes: •Clean rivers
•Fish & Wildlife•Flood control•Timber& Crops•Wetlands
MappedEcosystemServices
Projected and Quantified Bundles of Ecosystem
Services
Ecosystem Structure & Functioning
ProductionPoolsDecompositionFlowsAg-/De-gradationLand-Water
Interactions
•Cost•Optimization•Market Forces•Valuation
Water provisioning
Water Quality ERFs ETFs
FutureProjections
Research Targeted to Develop Ecological Response Functions (ERF) and Ecological Trade-off Functions (ETF)
W-ESP Decision Support System
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Changes in land useChanges in land use PollutionPollution Climate changeClimate change Invasive speciesInvasive species OverexploitationOverexploitation OtherOther
Direct drivers (forcing variables) of ecosystem changeDirect drivers (forcing variables) of ecosystem change
World Resources Institute
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Collaborators and StakeholdersCollaborators and Stakeholders
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31Drought Index Drought Index
Str
eam
Nit
rate
Drought Index
ERFs, ETFs Have Many DimensionsERFs, ETFs Have Many DimensionsExample 1:Example 1: soil texture modifies the effects of the 3 stressors at soil texture modifies the effects of the 3 stressors at
leftleft
FertilizationFertilization
TillageTillage
Water Water QualityQuality
CarbonCarbonSequestrationSequestration
Food Food ProductionProduction
Str
eam
Nit
rate
Tillage TillageTillage
Cro
p Y
ield
Soi
l Car
bonLow Sand%
High Sand%
?High Sand%
Low Sand%
? ?
High Sand%
Low Sand%
ClimateClimate
Str
eam
Nit
rate
N FertilizationN Fertilization
Cro
p Y
ield
N Fertilization
Soi
l Car
bon
Soi
l Car
bon
Cro
p Y
ield
Low Sand%
High Sand%
?
Low Sand%
High Sand%
?
Low Sand%
High Sand%
?
High Sand%
Low Sand%
?
Low Sand%
High Sand%
?
Low Sand%
High Sand%
?
Toggle with
previous slide
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Str
eam
Nit
rate
Drought Index
ERFs, ETFs Have Many DimensionsERFs, ETFs Have Many DimensionsExample 2: the 3 stressors at left have interactive effectsExample 2: the 3 stressors at left have interactive effects
Water Water QualityQuality
CarbonCarbonSequestrationSequestration
Food Food ProductionProduction
Str
eam
Nit
rate
N Fertilization
Low Tillage
High Tillage
?
N Fertilization
Cro
p Y
ield
Low Tillage
High Tillage
?
?
Cro
p Y
ield
Low Drought Index
?
Cro
p Y
ield
Tillage
High Drought Index
?
High N Fert
Low N Fert
?
Soi
l Car
bon
High N Fert
Low N Fert
Str
eam
Nit
rate
?
Tillage
Low Drought Index
High Drought Index Soi
l Car
bon
?
Tillage
Low Drought Index
High Drought Index
N Fertilization
Soi
l Car
bon
High Tillage
Low Tillage
?FertilizationFertilization
TillageTillage
High N Fert
Low N FertClimateClimate
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By 2013 ERP will complete site-specific demonstration projects that illustrate how regional and local managers can use alternative future scenarios to proactively conserve and enhance ecosystem goods and services in order to benefit human well-being and to secure the integrity and productivity of ecological systems.
Ecosystem Research Program LTG 5
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Place Based Sites
Tampa Bay – warm humid, 5 or so small watersheds, rapid urbanization, unique estuarine habitat, and high recreational use.
Midwest – temperate, multi-state, bread basket, biofuel production and processing pressures, many unique habitats.
Pacific Northwest – cool moist, strong policy and planning element for sustainable economic growth, focus on riparian forest.
Coastal Carolinas – warm humid, wetlands loss and sea level rise, impacts to sensitive habitats and protected species.
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Provides opportunities to:
Test similar methods in different locations
Look at urban to rural gradient
Evaluate variety of stressors
Research ways to upscale results
Develop coupled ecological/economic modeling/tools
Reach out to larger audience
Working Across Multiple Locations
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Land Value
Recreation Aesthetics
PotableWater
Human HealthEnergy
Food/Fiber
Cultural
ExistenceValue Flood
Control
ClimateMitigation
Contribution to Well Being
NutrientCycling
Productivity BiodiversityWater
QuantityWaterQuality
CarbonStorage
Sense ofPlace
What are the common functions and services across places?
What are the likely contributions to human well being?
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Biogeochemical Biogeochemical CyclingCycling
Carbon pool storagesCarbon pool storages standing biomassstanding biomass
soil organic contentsoil organic content
Carbon sequestrationCarbon sequestration net primary productionnet primary production
nitrificationnitrification Grams nitrogen / unit Grams nitrogen / unit area / unit timearea / unit time
Denitrification (in Denitrification (in rivers, lakes, rivers, lakes, reservoirs, wetlands)reservoirs, wetlands)
microbial abundance; microbial abundance; oxidation rate, (see oxidation rate, (see Wolheim and others for Wolheim and others for proxies)proxies)
Habitat / refugiaHabitat / refugia
TerrestrialTerrestrial nature, location, quantity & nature, location, quantity & arrangementarrangement
Fresh waterFresh water nature, location, quantity & nature, location, quantity & arrangementarrangement
EstuarineEstuarine nature, location, quantity & nature, location, quantity & arrangementarrangement
Near-coastal, marineNear-coastal, marine nature, location, quantity & nature, location, quantity & arrangementarrangement
BiodiversityBiodiversity Species countsSpecies counts
Air quality regulation Air quality regulation due to vegetation**due to vegetation**
Removal of pollutantsRemoval of pollutants
Micro-climate Micro-climate regulation due to regulation due to vegetationvegetation
Changes in diurnal Changes in diurnal temperature ranges from temperature ranges from backgroundbackground
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Disturbance & Disturbance & Natural Hazard Natural Hazard RegulationRegulation
Erosion ControlErosion Control kg/ha/year reducedkg/ha/year reduced
Flood ControlFlood Control Change in flood peaks (2-Change in flood peaks (2-yr., 10-yr., 50-yr. yr., 10-yr., 50-yr. recurrence interval)recurrence interval)
Fire ControlFire Control Fuel loadFuel load
Biological Biological RegulationRegulation
PollinationPollination Increased production due Increased production due to pollinatorsto pollinators
Pest ControlPest Control Diversity/distance from Diversity/distance from ideal/fragmentationideal/fragmentation
Disease ControlDisease Control Host vector habitatHost vector habitat
Food/Fiber Food/Fiber ProductionProduction
Plant crops (grains, Plant crops (grains, fruits, etfruits, et
Bushel /ha/yearBushel /ha/year
Animal proteinAnimal proteinTerrestrial (livestock)Terrestrial (livestock)
lbs/ha, animals/halbs/ha, animals/ha
Wild aquatic Wild aquatic (commercial fish)(commercial fish)
““yearling” estimates, yearling” estimates, catch, change in catch, catch, change in catch, change in fish advisorieschange in fish advisories
Grazing Forage Grazing Forage ProductionProduction
Livestock supported/ hay Livestock supported/ hay bale/habale/ha
Fuels Fuels Net energy production Net energy production
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Water provisioningWater provisioning
QualityQuality EMAP condition indicators EMAP condition indicators
Surface water storagesSurface water storages usable volume/capacityusable volume/capacity
GroundwaterGroundwater --maps of regional and alluvial --maps of regional and alluvial aquifersaquifers-- recharge rates per unit area-- recharge rates per unit area-- est’d. change in aquifer -- est’d. change in aquifer storage, or piezometric head., storage, or piezometric head., ft. above referenceft. above reference
Timing: Timing: Maintenance of base flowMaintenance of base flow
Statistical measures of baseflow Statistical measures of baseflow characteristics, and change in characteristics, and change in samesame
Hydrologic regime Hydrologic regime Statistical measures of flow Statistical measures of flow regime, and change in sameregime, and change in same
RecreationalRecreational
Hunting & FishingHunting & Fishing Licenses/takeLicenses/take
Ecotourism/Nature Viewing/ Ecotourism/Nature Viewing/ trekking/ campingtrekking/ camping
Visits /yearVisits /year
BoatingBoating Rentals/docking feesRentals/docking fees
Recreational SportsRecreational Sports RentalsRentals
Sense of placeSense of place Spatially explicit visualization of Spatially explicit visualization of change in landscape for selected change in landscape for selected service endpointsservice endpoints
Spiritual valueSpiritual value Spatially explicit estimates of Spatially explicit estimates of change in indigenous non-change in indigenous non-consumptive use service endpointsconsumptive use service endpoints
Existence value / behest Existence value / behest value value
Spatially explicit visualization of Spatially explicit visualization of change in landscape for selected change in landscape for selected service endpoints, including non-service endpoints, including non-consumptive use endpointsconsumptive use endpoints