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Ecosystem Diagnosis and Treatment (EDT) model for the Stillaguamish River Basin. Michael D. Purser, Senior Habitat Specialist Snohomish County Public Works Surface Water Management Everett, WA. Overview. EDT is a habitat rating model. - PowerPoint PPT Presentation
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Ecosystem Diagnosis and Treatment (EDT) model for the Stillaguamish River Basin
Michael D. Purser, Senior Habitat SpecialistSnohomish County Public Works Surface Water ManagementEverett, WA
Overview
• EDT is a habitat rating model.
• Data for 43 attributes are collected and the attributes are calculated or estimated for all reaches that are the habitat of Chinook salmon.
• The attributes include direct factors (e.g., large woody material, pool area, water quality, etc.), and indirect factors such as hydrology.
Model OutputsModel outputs include:
• a baseline report comparing current and historic Chinook salmon population performance
• an analysis of the relative importance of preservation and restoration actions in each subbasin, and
• a reach-scale analysis of the influence of specific actions on specific life history stages.
Attributes
•Default attribute values were created in an initial effort that was commissioned by the Tulalip Tribes and the WDFW (2002).
•New data were used to update attribute values such as physical habitat, water quality data, and riparian condition.
•TAG members reviewed the original dataset, the proposed changes, and the documentation supporting the revisions.
Fish Populations
• Spawning reaches and timing and harvest patterns are defined for both North Fork and South Fork Chinook salmon populations.
• The model predicts viable salmonid population parameters (VSP’s): ▫ life history diversity, ▫productivity, ▫capacity (maximum number of recruits
supportable), and ▫equilibrium abundance for returning spawners
and outmigrating smolts for both populations.
Baseline and Diagnostic Results
The initial results from the model include:1. an assessment of Current and Template
conditions on the VSP parameters (Baseline Report);
2. an analysis of benefits to each population of restoration and protection by subbasin; and
3. a reach-level analysis of the effect of attributes on the productivity of each life stage known to use the reach (Diagnostic Reports).
Actions and Scenarios
• EDT can model scenarios comprised of specific actions to see the effect on adult and juvenile Chinook salmon.
• The model was also used to confirm that the scenarios created would have benefit to the focal species.
• Actions modeled in EDT include: ▫riparian restoration, ▫floodplain connectivity/side-channel restoration, ▫reduction of sediment, and ▫restoration of large woody debris (in concert other
activities as well as stand-alone projects).
ResultsStillaguamish Baseline Report for SF, NF Chinook salmon populations.
Population ScenarioDiversity
index Productivity Capacity Abundance
NFStill Chinook
Current without harvest 58% 2.8 4,013 2,593
Current with harvest 55% 1.8 2,646 1,212
Historic potential 100% 15.6 26,339 24,653
SFStill Chinook
Current without harvest 40% 1.3 2,879 624
Current with harvest 11% 0.7 1,709 -
Historic potential 100% 14.4 22,116 20,581
Stilly Sediment Diagnosis
Population Scenario Diversity index Productivity Capacity Abundance
SFStill Chinook
Current without harvest 45% 1.4 3,028 861
SFSedDiagMSplusCanyonJim 66% 2.6 3,163 1,923
Historic potential 100% 14.6 21,820 20,329
SFStill Chinook
Current without harvest 40% 1.3 2,879 624
SFSedDiagMSplusCanyon 60% 1.8 2,967 1,320
Historic potential 100% 14 20,992 19,497
SFStill Chinook
Current without harvest 40% 1.3 2,879 624
SFSedDiagmsonly 57% 1.8 2,958 1,283
Historic potential 100% 14 20,992 19,497
NFStill Chinook
Current without harvest 58% 2.8 4,013 2,593
NFSedDiagwoDeer 58% 3.2 4,244 2,915
Historic potential 100% 15.6 26,339 24,653
NFStill Chinook
Current without harvest 58% 2.8 4,013 2,593
NFSedDiagwDeer 58% 3.1 4,290 2,902
Historic potential 100% 15.6 26,339 24,653
Diagnostic Reports – fall run (SF)•Protection priorities:
▫Jim Creek ▫Lower Pilchuck Creek
• Restoration priorities:• Lower Stillaguamish River, • Lower South Fork, and • Jim Creek
Diagnostic Reports – summer/fall run (NF)Protection priorities
▫French-Segelsen ▫Middle North Fork Stillaguamish
Restoration priorities ▫Lower North Fork, ▫Middle North Fork ▫French-Segelsen
Key Findings
•Reconnecting estuarine marsh had the largest response of any action.
•Riparian planting▫The long-term (25 years or more) benefits
of riparian planting increased productivity more than any other scenario.
▫Even in 10 years, planting yielded a significant increase in productivity and capacity through improvements in water quality.
Key Findings (cont’d)• Improve in-channel structure through placement
of LWD▫Wood has the most benefit where it changes the
distribution of habitat features (i.e., increase primary and backwater pools which are limiting throughout the system).
▫Important short-term measure because riparian plantings that may occur today will not contribute significant LWD for 50 years or more.
▫15-20% increase in productivity, capacity and abundance.
Key Findings (cont’d)•Reconnecting off-channel habitat
▫Significant for both populations assuming a large percentage of reconnected habitat becomes backwater pool with good food and cover. The effect of reconnection alone was relatively small because the area of off-channel habitat is small relative to the total reach area.
▫The effect was greater in the South Fork.