puget sound pressures assessment
TRANSCRIPT
Puget Sound Pressures Assessment (PSPA)
h2ps://sites.google.com/site/pressureassessment/home
Sco2 Redman Science & Evalua?on Program
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1. Which parts of Puget Sound ecosystem are most vulnerable to current pressures?
= parts of the ecosystem we care most about
Endpoints
PSPA helps us answer two ques?ons:
“Intrinsic Vulnerability” = endpoint’s vulnerability to one or more pressures
Lowland forests
Chinook
Large rivers
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2. Given endpoints of concern, what are the greatest pressures on the ecosystem?
Source Stressor contributes to or delivers
Pressure =
Development Land
conversion contributes to
Dams Altered flows contribute to
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Pressures Endpoints nega@vely impact
PuKng it all together …
Development Land
Conversion Unmanaged
lowland forests
Source + Stressor
contributes to
contributes to loss or degrada@on of ?
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Development Land
Conversion Unmanaged
lowland forests
Source + Stressor
contributes to
contributes to loss or degrada@on of
1. Which endpoints are most vulnerable to exis@ng stressors?
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2. Which stressors pose greatest risk to endpoints?
PSPA helps answer two ques?ons:
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Source
Source
Source
To answer those two quesIons for all the endpoints and stressors we care about in Puget Sound, we rate each specific Stressor -‐ Endpoint pair
Stressor Endpoint ?Look across all Stressor – Endpoint pairs to understand which endpoints are most vulnerable and which stressors pose greatest risk to Puget Sound
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How do we rate Stressor – Endpoint pairs?
Source
Source
Source Stressor
Endpoint
Intrinsic Vulnerability
SensiIvity
Intrinsic vulnerability modified by stressor intensity
Exposure
Is endpoint present?
How intense is stressor?
Poten?al Impact
= potenIal impact of stressor on endpoint within assessment unit
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= vulnerability of endpoint to stressor
Stressor intensity
Endpoint distribuIon
Assessments Units: Salmon Recovery Watersheds (16)
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Assessments Units: Marine Basins (7)
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PSPA submodels
Func?onal impact
Recovery ?me
Resistance
Stressor intensity
DistribuIon
Frequency
Strength
Sources
Endpoint distribuIon
Poten?al Impact
Intrinsic Vulnerability
Expert judgment GIS Analysis
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Submodel: Intrinsic Vulnerability How vulnerable is an endpoint to a stressor?
Ques?ons: 1. How resistant is the endpoint to the
stressor? 2. What is the func@onal impact of the
stressor on the endpoint? 3. How long does it take the endpoint to
recover?
Assump?ons: • No management of stressor • Stressor is acIng directly on endpoint • Stressor is strongly expressed
Intrinsic Vulnerability
Func?onal impact
Recovery ?me
Resistance
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Submodel: Stressor Intensity How intense is a stressor within an assessment unit?
Ques?ons:
1. How is the stressor distributed within the assessment unit?
2. How frequently does it occur? 3. How strongly is it expressed in the
assessment unit?
4. Which pressure sources contribute to the stressor?
Stressor intensity
DistribuIon
Frequency
Strength
Sources
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PSPA submodels: Scores are combined to determine Poten?al Impact
Func?onal impact
Recovery ?me
Resistance
Stressor intensity
DistribuIon
Frequency
Strength
Sources
Endpoint distribuIon
Poten?al Impact
Intrinsic Vulnerability
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Intrinsic vulnerability ! Most vulnerable endpoints ! Most potenIally significant stressors
Stressor intensity ! RelaIve intensity of each stressor across watersheds and
marine basins Where is each stressor the strongest? Where least strong?
So, what can PSPA results tell us?
Poten?al impact
Assessment-‐unit specific results (watershed or marine basin)
! Endpoint rankings ! Stressor rankings
Puget Sound-‐wide results
! Stressor and endpoint rankings
Stressor intensity
Poten?al Impact
Intrinsic Vulnerability
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! PrioriIze strategies for collecIve a]enIon • Sound-‐wide
• Across the breadth of the AcIon Agenda • Within topics, such as Strategic IniIaIves or ImplementaIon Strategies
• At scale of LIOs
! Inform funding prioriIes
! Focus monitoring (new & improved ) • Status & trends of pressures • EffecIveness of acIons to reduce pressures
! Inform research prioriIes • InvesIgate areas of high uncertainty in PSPA • Develop integrated models
How can we use these results?
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• Model-‐based
• Criteria-‐driven evaluaIon • SystemaIc accounIng for uncertainty • Expert judgments & GIS-‐based analysis
! Update the 2009 Puget Sound regional threats raIng
PSPA Process summary:
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Next slides compare 2009 results to 2014 results
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2009 Highly Rated Threats
• Climate change
• ResidenIal, commercial, port, shipyard development
• Runoff from the built environment
• Shoreline armoring
• Roads, transportaIon, uIlity infrastructure
• Dams, levees, Idegates
• Invasive species • Animal harvest
Very High
High
Very high Land cover conversion for transporta@on & u@li@es for residen@al, commercial, industrial for natural resource produc@on
Nonpoint source polluIon toxic chemicals conven@onal pollutants
Shoreline hardening
High Large spills Point source polluIon Changing ocean condiIon Spread of disease and pathogens
to na@ve species human pathogens
Timber harvest
Moderate Altered low and peak flows Shading of shallow water habitat Structural barriers to flow Marine species disturbance
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Candidate priority stressors for PSP based on PSPA results for Vital Sign endpoints
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2009 Highly Rated Threats
Climate change
ResidenIal, commercial, port, shipyard development
Runoff from the built environment
Shoreline armoring
Roads, transportaIon, uIlity infrastructure
Dams, levees, Idegates
Invasive species
Animal harvest
Very High
High
Changing ocean condi?on
Land cover conversion: Development Land cover conversion: Transporta?on & u?li?es Shoreline hardening
Very High
High
Land cover conversion: natural resource produc@on Nonpoint source pollu@on: toxic chemicals Nonpoint source pollu@on: conven@onal pollutants
Large spills Point source pollu@on Spread of disease & pathogens to na@ve species Spread of human disease and pathogens
Shading of shallow water habitat Marine species disturbance Timber harvest
Moderate
2014 PSPA Highly Rated Stressors (to Vital Signs)
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Next slides show a few different ways to present informaIon about endpoints, Vital Signs and PSPA results
• Small, high-‐gradient streams • Headwater slope wetlands • Headwater depressional
wetlands • Lakes and ponds • Large rivers • Large streams • Small, low-‐gradient streams • Lowland slope wetlands • Lowland depressional
wetlands • Freshwater Idal wetlands • Riparian vegetaIon
• LoIc benthic invertebrates • LoIc aquaIc vertebrate
communiIes • AquaIc plant communiIes • Chinook salmon • Coho salmon • Cu]hroat trout • Kokanee • Bald eagle • River o]er • Freshwater mussels
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Endpoints Marine-‐nearshore Terrestrial Freshwater
• Alpine grassland and shrublands
• Subalpine unmanaged forests • Subalpine managed forest • Unmanaged lower elevaIon
forests • Managed lower elevaIon
forests • Oregon white oak woodlands • Lowland grasslands • Agriculture areas • Urban open space • Forest interior birds • Pond breeding amphibians
associated with upland forest • Forest salamanders • Bobcat • Roosevelt elk • Coopers Hawk • Long-‐legged myoIs bats and
Keen’s myoIs bats
• River deltas • Beaches • Embayments • Rocky shores • Open water • Eelgrass, kelp, and other
submerged vegetaIon communiIes
• Herring • Surf smelt • Rockfish (adult) • Benthic community • Epibenthic community • Pelagic community • Demersal fish and
invertebrate community • Mobile benthic
carnivores • Sessile filter feeders • Chum and pink salmon • Rhinoceros auklet • Killer whale
HA
BIT
ATS
SPEC
IES
• Small, high-‐gradient streams • Headwater slope wetlands • Headwater depressional
wetlands • Lakes and ponds • Large rivers • Large streams • Small, low-‐gradient streams • Lowland slope wetlands • Lowland depressional
wetlands • Freshwater Idal wetlands • Riparian vegetaIon
• LoIc benthic invertebrates • LoIc aquaIc vertebrate
communiIes • AquaIc plant communiIes • Chinook salmon • Coho salmon • Cu]hroat trout • Kokanee • Bald eagle • River o]er • Freshwater mussels
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Endpoints orange = lower rated in all results Marine-‐nearshore Terrestrial Freshwater
• Alpine grassland and shrublands
• Subalpine unmanaged forests • Subalpine managed forest • Unmanaged lower elevaIon
forests • Managed lower elevaIon
forests • Oregon white oak woodlands • Lowland grasslands • Agriculture areas • Urban open space • Forest interior birds • Pond breeding amphibians
associated with upland forest • Forest salamanders • Bobcat • Roosevelt elk • Coopers Hawk • Long-‐legged myoIs bats and
Keen’s myoIs bats
• River deltas • Beaches • Embayments • Rocky shores • Open water • Eelgrass, kelp, and other
submerged vegetaIon communiIes
• Herring • Surf smelt • Rockfish (adult) • Benthic community • Epibenthic community • Pelagic community • Demersal fish and
invertebrate community • Mobile benthic
carnivores • Sessile filter feeders • Chum and pink salmon • Rhinoceros auklet • Killer whale
HA
BIT
ATS
SPEC
IES
• Small, high-‐gradient streams • Lakes and ponds • Large rivers • Large streams
• Small, low-‐gradient streams
• Freshwater Idal wetlands • Riparian vegetaIon
• LoIc benthic invertebrates
• Chinook salmon • Coho salmon • Cu]hroat trout • Kokanee
• Unmanaged lower elevaIon forests • Managed lower elevaIon forests
• Forest interior birds
• River deltas
• Beaches • Embayments
• Open water
• Eelgrass, kelp, and other submerged vegetaIon communiIes
• Herring
• Rockfish (adult) • Benthic community
• Demersal fish and invertebrate community
• Mobile benthic carnivores • Sessile filter feeders • Chum and pink salmon
• Rhinoceros auklet
• Killer whale 24
Estuaries
Eelgrass
Herring
Orcas
Chinook
Land cover
RecreaIonal fishing
Birds
Swimming beaches
Freshwater quality
Marine water
Marine sediment
BIBI
Floodplains
Streamflow
Toxics in fish
PSP Vital Signs represented by Endpoints
Shellfish beds
• Headwater slope wetlands • Headwater depressional
wetlands • Lowland slope wetlands • Lowland depressional
wetlands
• LoIc aquaIc vertebrate communiIes
• AquaIc plant communiIes • Bald eagle • River o]er • Freshwater mussels
• Alpine grassland and shrublands
• Subalpine forests • Oregon white oak woodlands • Lowland grasslands • Agriculture areas • Urban open space
• Pond breeding amphibians associated with upland forest
• Forest salamanders • Bobcat • Roosevelt elk • Coopers Hawk • Long-‐legged myoIs bats and
Keen’s myoIs bats
• Rocky shores
• Surf smelt • Epibenthic community • Pelagic community
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Endpoints not represented by PSP Vital Signs Blue = endpoints rated High -‐ Very High but not addressed with Vital Signs
! Consider for Vital Signs or monitoring?
Orange = endpoints rated Low – Moderate and not addressed with Vital Signs
Marine-‐nearshore Terrestrial Freshwater
• Small, high-‐gradient streams • Headwater slope wetlands • Headwater depressional
wetlands • Lakes and ponds • Large rivers • Large streams • Small, low-‐gradient streams • Lowland slope wetlands • Lowland depressional
wetlands • Freshwater Idal wetlands • Riparian vegetaIon
• LoIc benthic invertebrates • LoIc aquaIc vertebrate
communiIes • AquaIc plant communiIes • Chinook salmon • Coho salmon • Cu]hroat trout • Kokanee • Bald eagle • River o]er • Freshwater mussels
• Alpine grassland and shrublands
• Subalpine unmanaged forests • Subalpine managed forest • Unmanaged lower elevaIon
forests • Managed lower elevaIon
forests • Oregon white oak woodlands • Lowland grasslands • Agriculture areas • Urban open space • Forest interior birds • Pond breeding amphibians
associated with upland forest • Forest salamanders • Bobcat • Roosevelt elk • Coopers Hawk • Long-‐legged myoIs bats and
Keen’s myoIs bats
• River deltas • Beaches • Embayments • Rocky shores • Open water • Eelgrass, kelp, and other
submerged vegetaIon communiIes
• Herring • Surf smelt • Rockfish (adult) • Benthic community • Epibenthic community • Pelagic community • Demersal fish and
invertebrate community • Mobile benthic
carnivores • Sessile filter feeders • Chum and pink salmon • Rhinoceros auklet • Killer whale
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Estuaries
Shellfish beds
Eelgrass
Herring
Orcas
Chinook
Birds
Land cover
RecreaIonal fishing
Birds
Swimming beaches
Freshwater quality
Marine water Marine
sediment
BIBI
Floodplains
Streamflow
Toxics in fish
Endpoints that represent PSP Vital Signs
Commercial fishing
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GeKng into the details of the results …
Uncertainty 28
Stressor contribuIon to Intrinsic Vulnerability: all Vital Sign endpoints
Land cover converted for development (com/res/ind)
Land cover converted for transporta?on & u?li?es
Large spills
Persistent toxics Land cover converted for natural resource produc?on
Conven?onal pollutants
Non-‐persistent toxics
Changing ocean condi?on
Pathogens and disease
Shoreline hardening
Altered peak flows
Altered low flows
Structural barriers to flow of water, sediment, etc. St
ressor con
tribuI
on to
vulne
rability
Highest contribuIon to V.S. vulnerability
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Stressor
Summed Stressor Index Very High or High
Count of Assessment Units with Very High or High Stressor Index
Marine Basins Watersheds Marine Basins Watersheds
Conversion of land cover for natural resource producIon
Very High Very High 4 11
Non-‐point source, persistent toxic chemicals in aquaIc systems
Very High High 3 14
Non-‐point source convenIonal water pollutants
High Very High 1 16
Conversion of land cover for transportaIon & uIliIes
High High -‐ 7
Shoreline hardening High High 4 8
Shading of shallow water habitat Very High lower 4 -‐
Conversion of land cover for residenIal, commercial, and industrial use
moderate High 1 6
IntroducIon, spread, or amplificaIon of human pathogens
High lower 3 -‐
Species disturbance – marine High -‐ 4 -‐
Spread of disease and parasites to naIve species
High lower 2 -‐
Changing ocean condiIon High -‐
Timber harvest -‐ moderate -‐ 8
Poten?al Impact of Stressor on all Vital Sign endpoints
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Key Stressors to Vital Sign endpoints: Watersheds poten@al impact + intrinsic vulnerability
Land cover conversion
Non-‐point pollu?on
Large spills
Point source pollu?on
Shore hardening
Structural barriers to flow
Timber harvest
PotenIal Impact for Vital Sign Endpoints
Intrinsic Vu
lnerability fo
r Vital Sign Endp
oints
Peak flows Low flows
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Key Stressors to Vital Sign endpoints: Nisqually Watershed poten@al impact + intrinsic vulnerability
Land cover conversion
Non-‐point pollu?on
Large spills
Point source pollu?on
Shore hardening
Structural barriers to flow
Timber harvest
PotenIal Impact for Vital Sign Endpoints
Intrinsic Vu
lnerability fo
r Vital Sign Endp
oints
Peak flows Low flows
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Key Stressors to Vital Sign endpoints: Marine Basins poten@al impact + intrinsic vulnerability
PotenIal Impact for Vital Sign Endpoints
Intrinsic Vu
lnerability fo
r Vital Sign Endp
oints
Land cover conversion
Non-‐point pollu?on
Large spills
Point source pollu?on
Spread of disease & pathogens
Shore hardening
Structural barriers to flow
Changing ocean condi?on
Shading of shallow water
Marine species disturbance
Low flows
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Key Stressors to Vital Sign endpoints: South Sound (marine) poten@al impact + intrinsic vulnerability
PotenIal Impact for Vital Sign Endpoints
Intrinsic Vu
lnerability fo
r Vital Sign Endp
oints
Land cover conversion
Non-‐point pollu?on
Large spills
Point source pollu?on
Spread of disease & pathogens
Shore hardening
Structural barriers to flow
Changing ocean condi?on
Shading of shallow water Marine
species disturbance
Low flows
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Priority Stressors to PSP Vital Signs
Overall RaIng Stressor Intrinsic Vulnerability PotenIal Impact
Very high Land cover conversion for transporta@on & u@li@es for residen@al, commercial, industrial for natural resource produc@on
Nonpoint source polluIon toxic chemicals conven@onal pollutants
Shoreline hardening
Very High Very High High
Very High High High
High High/Mod Very High
Very High Very High High
High Large spills Point source polluIon Changing ocean condiIon Spread of disease and pathogens
to na@ve species human pathogens
-‐ -‐ -‐ Medium
-‐ -‐ High
High High
Moderate Shading of shallow water habitat Marine species disturbance Timber harvest
-‐ -‐ -‐
Very High High Moderate
I pulled these from other slides. May not be correct.
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Stressor Intensity: Marine Basins C. SHORELINE ARMORING
! PSNERP GIS: % armored shoreline (length)
! Frequency = Permanent
! Intensity range: 0.16 (North Central) -‐ 1.0 (South Central)
What does this mean?
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! CCAP 2011 GIS: % land area = "developed“
! Frequency = Permanent
! Intensity range: 0.04 (Elwha) – 1.0 (Lake Washington/ Cedar/ Sammamish)
Stressor Intensity: Watersheds A1. LAND COVER CONVERSION FOR DEVELOPMENT (RES, COM, IND)
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! PrioriIze strategies for collecIve a]enIon • Sound-‐wide
• Across the breadth of the AcIon Agenda • Within topics, such as Strategic IniIaIves or
ImplementaIon Strategies
• At scale of LIOs
! Inform funding prioriIes
! Focus monitoring (new & improved ) • Status & trends of pressures • EffecIveness of acIons to reduce pressures
! Inform research prioriIes • InvesIgate areas of high uncertainty in PSPA • Develop integrated models
How can we use these results?