Project Level Effectiveness Monitoring in the Estuary and Response in Fish Communities.

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Presentation transcript:

Project Level Effectiveness Monitoring in the Estuary and Response in Fish Communities

Who is CREST? Council of Governments (b. 1974) Council of Governments (b. 1974) Members: Port of Astoria, Wahkiakum Port Dist. #2, Port of Peninsula, Port of Ilwaco, City of Seaside, City of Warrenton, City of Astoria, City of Gearhart, City of Ilwaco, Clatsop County, Wahkiakum County, Clatsop Soil & Water Dist., City of Cannon Beach Members: Port of Astoria, Wahkiakum Port Dist. #2, Port of Peninsula, Port of Ilwaco, City of Seaside, City of Warrenton, City of Astoria, City of Gearhart, City of Ilwaco, Clatsop County, Wahkiakum County, Clatsop Soil & Water Dist., City of Cannon Beach

CREST DEPARTMENTS: 1. Coastal/Estuarine Planning 2. Habitat Restoration 3. Ecosystem Monitoring Project Types: -dike breach -riparian enhancement -stream realignment -culvert/bridge replacement -in-stream enhancements

Effectiveness Monitoring

Fish Community Parameters Fish Community Parameters Species Species Abundance Abundance Length Length Weight Weight Additional Parameters Additional Parameters Genetics Genetics Prey Availability * Prey Availability * Prey Utilization * Prey Utilization * Residence Time Residence Time *lab analyses at AHS Tributary & Mainstem Baseline Seining Restoration & Reference Site Fyke Net Trap Insect Fallout Traps & Gastric Lavage

Habitat Parameters Habitat Parameters Water Quality Water Quality Vegetation Vegetation Sediment Accretion Sediment Accretion Hydrology (channel formation) Hydrology (channel formation) Sampling Design Sampling Design Before & After Before & After Comparison to baseline Comparison to baseline Comparison to Comparison to reference sites reference sites

Coordinated Regional Effort AEM for individual restoration projects (EP Coordination, BPA funding) NOAA Fisheries (multiple sites) NOAA Fisheries (multiple sites) CREST, Columbia Land Trust, Scappoose Bay Watershed Council. Ash Creek Forest Management, Parametrix CREST, Columbia Land Trust, Scappoose Bay Watershed Council. Ash Creek Forest Management, Parametrix Cumulative Effects Study (USACE funding) Measuring hydrology, channel morphology, vegetation, fish presence and community structure, and flux of nutrients and organic matter Measuring hydrology, channel morphology, vegetation, fish presence and community structure, and flux of nutrients and organic matter Developing monitoring protocols (Roegner et al. 2008) Developing monitoring protocols (Roegner et al. 2008) Reference Site Study (EP & PNNL Coordination, BPA funding) Measuring hydrology, channel morphology, vegetation, elevation profiles, and sediment accretion Measuring hydrology, channel morphology, vegetation, elevation profiles, and sediment accretion Coordination to ensure: Data are comparable across sites and time for similar types of actions and habitats Data are comparable across sites and time for similar types of actions and habitats Results are scalable Results are scalable

Spring 2008: Selection of Pilot AEM Sites (EP Science Workgroup, BPA funding) Developed a list of sites: Developed a list of sites: Multi year restoration projects had occurred Multi year restoration projects had occurred Some baseline monitoring was conducted Some baseline monitoring was conducted  Number of potential sites = 12 Intensive versus Extensive Intensive versus Extensive Selected 4 sites representing project diversity Selected 4 sites representing project diversity Different river reaches, habitat types, and restoration strategies Different river reaches, habitat types, and restoration strategies Solicited feedback on sites from scientific working groups Solicited feedback on sites from scientific working groups

Fort Clatsop Fort Clatsop Brackish freshwater wetland Brackish freshwater wetland Culvert replacement with bridge Culvert replacement with bridge Scappoose Bottomlands Scappoose Bottomlands Emergent wetland Emergent wetland Revegetation, Cattle exclusion Revegetation, Cattle exclusion Sandy River Delta Sandy River Delta Floodplain forest Floodplain forest Revegetation Revegetation Mirror Lake Mirror Lake Bottomland riparian forest Bottomland riparian forest LWD, Culvert enhancement, Revegetation LWD, Culvert enhancement, Revegetation

Watershed Context Seaside Dike Breach II Seaside Dike Breach I South Slough Bridge Install Otter Point Dike Breach Extensive diking for flood control and agriculture Dredging and removal of woody debris to fill lands and aid navigation Pesticide and fertilizer use Runoff and sedimentation from logging operations and road building Encroaching development Erosion & poor riparian cover

-Restore tidal processes -Reconnect 50 acres of historic off-channel rearing habitat -Minimize risk to County Rd. Fort Clatsop’s South Slough

South Slough Salmonid Abundance South Slough Pre-construction (2007) Post-Construction (2008) Post-Construction (2009) Reference Site (2009)

Salmonid Average Lengths 2008 Date Chinook salmon ChumCohoSteelhead Cutthroat Trout 6-Mar43* 20-Mar38 3-Apr32 17-Apr10450*192* 1-May May43 30-May Jun Jun Jul51*73*78* 24-Jul69 4-Aug127* 22-Aug69 * Indicates individual length measurement

Prey Availability & Utilization

Juvenile salmon occupy restoration sites in accordance with their life histories; similar abundances in restored marshes compared to mainstem tributaries. Juvenile salmon occupy restoration sites in accordance with their life histories; similar abundances in restored marshes compared to mainstem tributaries. Juvenile salmon are utilizing the dominant prey types available in the site. Juvenile salmon are utilizing the dominant prey types available in the site. Recruitment & migration corridor factors, as well as site maturity, may control variability in fish populations. Recruitment & migration corridor factors, as well as site maturity, may control variability in fish populations. Site Specific Lessons:

Meta-Analysis of Data for Monitoring Programs Literature Search Literature Search Contact restoration & monitoring partners for data Contact restoration & monitoring partners for data Identify sites with comparable Identify sites with comparable restoration actions & pre/post data Compile data on select metrics Compile data on select metrics Select analyses methods and apply Select analyses methods and apply Preliminary meta-analysis metrics: Preliminary meta-analysis metrics: Water temperature Water temperature Sediment accretion rate Sediment accretion rate Juvenile salmon presence/absence Juvenile salmon presence/absence Photo points Photo points

Reference Sites Monitoring Sites Restored Sites Performance (Report Cards) Program Report Card Lesson Learned (Meta Analysis) Proposed Project Prioritization Analysis Project RFP Stakeholders Report New Science Cumulative Effects Research Restoration Site EffectivenessData Project Proposals New Projects Restoration Strategy

Meta-Analysis Sites Ft. Clatsop Johnson Property Kandoll Farm Vera Slough Crims Is. 5 sites chosen Tidal reconnection projects (dike breach, culvert & tide gate replacements) Restoration actions between

Data Available *Used in preliminary meta-analysis

Pre Post Pre Post Vegetation Photo Points: South Slough

Water Temp: South Slough Result: Water temperatures were lower post restoration

Sediment Accretion Rates Restoration Site Reference Site Crims Is. [1] [1] Ft. Clatsop [2] [2] Johnson Property [3] [3] Kandoll Farm [4] [4] Vera Slough ---- [1] [1] Measurements taken September 2006 and February 2007 [2] [2] Measurement taken July 24, 2008 (restoration) 8/15/08 (reference). [3] [3] Measurements taken 2005 and [4] [4] Measurements taken 2005 and Sediment Accretion Rates (cm y-1) at Paired Restoration & Reference Sites

Salmon Presence Pre-RestorationPost-Restoration Crims Is. NoYes Ft. Clatsop Yes (sparse) Yes (abundant) Johnson Property NoYes Kandoll Farm NoYes Vera Slough NoNo 4 of 5 sites demonstrated increased fish presence post project implementation Vera Slough outside of migratory pathway?

Summary--Is the response variable trending in the desired direction?

Take Home Message Long-term monitoring data is invaluable Long-term monitoring data is invaluable Variability in level of effort / metrics between sites limit analyses Variability in level of effort / metrics between sites limit analyses Pre/post project implementation bare minimum Pre/post project implementation bare minimum >10 year per site preferable to get long-term trajectory >10 year per site preferable to get long-term trajectory Include report cards Include report cards lists project objectives and expected outcomes lists project objectives and expected outcomes monitoring data results then document whether objectives were met monitoring data results then document whether objectives were met Restored sites are responding measurably to restoration actions on individual site scale Restored sites are responding measurably to restoration actions on individual site scale Differences in response among sites, for example temperature and accretion rates, can likely be explained by differences in geomorphology, elevation and location Differences in response among sites, for example temperature and accretion rates, can likely be explained by differences in geomorphology, elevation and location Important considerations in assessing cumulative effects on large scale Important considerations in assessing cumulative effects on large scale How much is enough…and where should we focus our limited resources for biggest uplift are difficult questions How much is enough…and where should we focus our limited resources for biggest uplift are difficult questions

Thank you! Contacts for More Information: Micah Russell (503) ext 18, Catherine Corbett (503) ext 240, Heida L. Diefenderfer (360) , Blaine D. Ebberts (503) , Gary E. Johnson (503) , Krista L. Jones (503) ext 239, Ian Sinks (360) ,