Habitat Enhancement Effectiveness – Biological Monitoring & Evaluation VII

Salmonid Research, Monitoring, and Evaluation (RM&E)

Monitoring Research
Project ID18-Umat-03
Recovery DomainsMiddle Columbia River
Start Date06/01/2019
End Date02/29/2024
Year2018
StatusCompleted
Last Edited08/07/2024
 
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Description    


The overall goal of the CTUIR biomonitoring program is to evaluate the effectiveness of CTUIR stream restoration efforts in respect to aquatic biota, particularly spring Chinook salmon, summer steelhead, and bull trout populations. The project seeks to assess the biological outcomes of a wide range of restoration efforts in the ceded territory of the Umatilla, Grande Ronde, John Day, Walla Walla and Tucannon subbasins. CTUIR’s approach to habitat restoration is based in the framework of the Umatilla River Vision where Geomorphology, Hydrology, Connectivity, Riparian Vegetation, and Aquatic Biota are identified as the key touchstones vital to a healthy river ecosystem and essential to the re-naturalization of the tribal First Foods. CTUIR utilizes this framework to identify and design holistic restoration projects that seek to restore floodplain function as it is described in the River Vision and address the primary limiting habitat factors in association with each of the identified touchstones.



To date this project has been predominantly the physical monitoring component complementary of the CTUIR Biomonitoring Plan with site level fish and macroinvertebrate response monitoring. Current monitoring includes Columbia Habitat Monitoring and BPA programmatic Action Effectiveness Monitoring (AEM) habitat monitoring protocols in combination with biological data to provide detailed site scale fish/habitat relationship information comparable on a regional level. Continued emphasis on monitoring the physical limiting factors addressed by CTUIR restoration actions is critical in informing managers and implementers for guiding future restoration efforts.



With the increasing size and ambition of fisheries habitat restoration projects, CTUIR requires scalable field and remote monitoring tools to measure the results of these actions. CTUIR has utilized the CHaMP/AEM habitat protocol along with several biological measures to assess baseline and post stream restoration conditions to this point.



This project continues this multiyear effort, and includes the second part of a three part research endeavor to review the CHaMP/AEM protocol alongside the Physical Habitat Monitoring Strategy developed by CTUIR in 2015. PHaMS emphasizes remote sensing methods at larger scale restoration projects. Incorporating the methodologies and efficiencies from the two separate protocols into a site by site specific monitoring plan will be the ultimate goal.



This seventh year project provided a cost share for BPA funding in order to help meet the objectives of the CTUIR biomonitoring program, through training to benefit the continued habitat monitoring and a research endeavor to design a future monitoring strategy for large floodplain restoration projects. As well as a continuation and extension of a long term macroinvertebrate study designed around the restoration efforts. The ability to detect biological changes in response to habitat restoration is critical for determining habitat quantity and quality, and to understand what particular restoration action or suite of actions yield the greatest biological response.



Work in 2019 included continued site level habitat monitoring of three sample locations within Meacham Creek (permanent technician time funded by BPA, training funded by PCSRF). Juvenile salmonid abundance surveys at each sample site during summer and fall seasons (permanent technicians funded by BPA). Collaboration of redd abundance surveys for spring Chinook and summer steelhead conducted throughout the Meacham tributary March-September (permanent technicians funded by BPA). Continuation of Meacham macroinvertebrate study through OSU subcontract (PCSRF funded). Continuation of the CHaMP/PHaMS methodology review and metric comparison with collection and processing of data (PCSRF funded).

Project Benefit    


The Confederated Tribes of the Umatilla Indian Reservation (CTUIR) is implementing a habitat restoration program with emphasis on reducing the effects of primary limiting factors (i.e. water temperature and habitat complexity) and restoring natural ecological processes. Biomonitoring sample sites have been selected for evaluating a biological response to habitat restoration; and the expected benefit is to improve habitat quality for adult holding and spawning, and juvenile rearing of fish species of interest. Monitoring habitat in parallel with fish surveys can provide valuable information regarding fish/habitat relationships.

Accomplishments

Metric Completed Originally
Proposed
Research and Monitoring
  Stream Miles Monitored 19.00 19.00

Funding Details

SourceFunds
PCSRF$50,000
Other$84,468
Report Total:$134,468


Project Map



Worksites

Meacham Creek    


  • Worksite Identifier: Meacham Creek
  • Start Date: 06/01/2019
  • End Date: 02/29/2024
Area Description

No Area Description data was found for this worksite.

Location Information

  • Basin: Middle Columbia (170701)
  • Subbasin: Umatilla (17070103)
  • Watershed: Meacham Creek (1707010302)
  • Subwatershed: Boston Canyon-Meacham Creek (170701030206)
  • State: Oregon
  • Recovery Domain: Middle Columbia River
  • Latitude: 45.64666667
  • Longitude: -118.3605555

ESU

  • Mid-Columbia River Spring-run Chinook Salmon ESU
  • Middle Columbia River Steelhead DPS
  • Un-Named ESU Bull Trout

Map

Photos

Metrics

Metrics
  • E.0 Salmonid Research, Monitoring, and Evaluation (RM&E)Y (Y/N)
    •      . . E.0.a RM&E Funding 134,468.00
    •      . . E.0.b
      Complement habitat restoration project
      CTUIR Umatilla Anadromous Fish Habitat project (# 1987-100-01)
    •      . . E.0.c
      Project identified in a plan or watershed assessment.
      Biological Effectiveness Monitoring and Evaluation Plan for Fisheries Habitat Enhancement in CTUIR Subbasins (Stillwater Sciences 2011b)
    •      . . E.0.d.1 Number of Cooperating Organizations 1
    •      . . E.0.d.2
      Name Of Cooperating Organizations.
      Oregon State University (OSU) Extension Service
    •      . . E.0.e.1 Number of reports prepared 1
    •      . . E.0.e.2
      Name Of Report
      CTUIR Habitat Enhancement Effectiveness Project Final Report
    •      . . E.1 MonitoringY (Y/N)
      •      . . . . E.1.a Monitoring funding 75,533.00
      •      . . . . E.1.b.1 Stream Miles Monitored 19.00
      •      . . . . E.1.b.2 Acres of Watershed Area Monitored 37.9
      •      . . . . E.1.b.3 Square miles of water monitored1 (Square miles)
      •      . . . . E.1.c.2 Salmonid smolt or fry monitoringY (Y/N)
        •      . . . . . . E.1.c.2.a # miles (to nearest 0.01 mile) monitored for Salmonid smolt or fry 1.20
      •      . . . . E.1.c.3 Biological instream monitoring (other than salmon)Y (Y/N)
        •      . . . . . . E.1.c.3.a # miles (to nearest 0.01 mile) monitored for Biological indicies (other than salmon) 19.00
      •      . . . . E.1.c.4 Redd countsY (Y/N)
        •      . . . . . . E.1.c.4.a # miles (to nearest 0.01 mile) monitored for redds 19.00
      •      . . . . E.1.c.5 Carcass countsY (Y/N)
        •      . . . . . . E.1.c.5.a # miles (to nearest 0.01 mile) monitored for Carcasses 19.00
      •      . . . . E.1.c.8 Water quality monitoringY (Y/N)
        •      . . . . . . E.1.c.8.a # miles (to nearest 0.01 mile) of stream monitored for water quality 10.50
      •      . . . . E.1.c.13 Restoration effectiveness monitoringY (Y/N)
        •      . . . . . . E.1.c.13.a # miles (to nearest 0.01 mile) of stream or streambank monitored 1.20
        •      . . . . . . E.1.c.13.c # acres (to nearest 0.1 acre) monitored 37.9
      •      . . . . E.1.c.14 Restoration validation monitoringY (Y/N)
        •      . . . . . . E.1.c.14.a # miles (to nearest 0.01 mile) stream or streambank monitored 1.20
        •      . . . . . . E.1.c.14.c # acres (to nearest 0.1 acre) monitored 37.9
        •      . . . . E.1.d
          Name Of Comprehensive Monitoring Strategy/Program
          CTUIR and ODFW. 2004. Umatilla Subbasin Plan, Northwest Power Planning Council. www.nwpcc.org CTUIR and ODFW. 2006. Comprehensive Research, Monitoring, and Evaluation Plan for the Umatilla sub-basin for summer steelhead and Chinook salmon. Confederated Tribe of the Umatilla Indian Reservation, Pendleton, OR and the Oregon Department of Fish and Wildlife, Hermiston, OR. Jones, K. L., O'Daniel, S. J., Beechie, T. J., Zakrasjek, J., & Webster, J. G. (2015). Physical Habitat Monitoring Strategy (PHAMS) for reach-scale restoration effectiveness monitoring. Reston, Virginia: U.S. Geological Survey.
        •      . . . . E.1.e
          Description of monitoring
          The scope of the CTUIR biomonitoring plan includes the direct measurement of habitat improvements which will provide an understanding of the benefits of systematically collecting habitat data in conjunction with biological data in order to gain the greatest understanding of relationships between fish abundance, growth, migration timing, and survival as they relate to stream habitat restoration actions. Our strategy uses regionally standardized habitat protocols (Columbia Habitat Monitoring Program, CHaMP) to sample project reaches pre and post habitat restoration in contrast to unmodified control reaches. CHaMP methods provide standardized metrics that can be used to measure response variables in salmonid habitat. Habitat surveys consist of a simultaneous topographical and auxiliary data survey. CTUIR is congruently monitoring juvenile fish abundance and species composition at each site using snorkel methods. Benthic macroinvertebrate samples are collected yearly at each location. Adult redd enumerations and carcass counts for focal species are primarily conducted by basin M and E programs with some supplemented help from this project. Increased aquatic and terrestrial invertebrate samples will also be paired with habitat data this year. CTUIR implements site level habitat surveys using a combination of CHaMP and AEM data collection methodology. Habitat surveys consist of a simultaneous topographical and auxiliary data survey. Auxiliary data is collected at the channel unit, transect, and site level. The topographic survey is processed through a suite of GIS tools created for the CHaMP program (Bouwes, 2011). A composite sample of benthic macroinvertebrates are accrued for each treatment and control site using a method derived from the Environmental Monitoring and Assessment Program (EMAP) targeted riffle sampling protocol. Standard lab analysis and index values are derived for each benthic sample including; biomass, taxa richness, Hilsenhoff Biotic Index (HBI), and Oregon PREDictive (PREDATOR) model results. Adult Spawning Abundance and Distribution www.monitoringresources.org/Document/Protocol/Details/3322 Adult spawning abundance and distribution is estimated based on redd and carcass counts conducted in the treatment and control reaches. Coordination with other monitoring entities (ODFW and WDFW) occurs annually in order to minimize data collection overlap. Most data utilized for this analysis is collected under other CTUIR and State projects through Status and Trend Monitoring. Sampling occurs annually commencing at the onset of the spawning season and continues approximately every 10/14 days until spawning is complete (Gallagher 2007). Data derived from redd count surveys include: 1.Spatial spawning distribution 2.Temporal spawning distribution Juvenile Fish Abundance Snorkeling www.monitoringresources.org/Document/Protocol/Details/3324 Juvenile fish abundance is obtained through snorkel surveys of treatment and control reaches. Juvenile snorkel surveys are conducted for the entirety of each treatment and control at site level. Species, size class (10mm accuracy), habitat unit, and instream structure usage are recorded for each fish throughout the reach (Crawford 2011). Data derived from snorkel surveys include: 1.Juvenile fish density and abundance (fish/m2) 2.Life history diversity within a site 3.Fish use of available habitat structures pre and post treatment Habitat Complexity Effects on Aquatic and Terrestrial Biota We plan to pair detailed field habitat surveys at each site with following: 1.Aquatic benthic macroinvertebrates samples (kick nets) 2.Terrestrial invertebrate samples (pitfall traps and transect surveys of orb-weaving spiders) 3.Emergent aquatic plant data (cover and diversity, small samples taken for laboratory identification) 4.Leaf litter input 5.Leaf litter retention 6.In addition we are considering adding amphibian (spotted frog) surveys
      •      . . E.2 ResearchY (Y/N)
        •      . . . . E.2.a Research Funding 58,935.00
        •      . . . . E.2.b.1 Modeling and data analysisY (Y/N)
          •      . . . . . . E.2.b.1.a
            Key issues addressed by modeling and data analysis research
            Reach scales (100s to 1000s of meter stream lengths) are now commonly manipulated by CTUIR Fisheries Habitat Projects (ex. Meacham Creek, Catherine Creek, Rock Creek, Tucannon River). With the increasing size and ambition of fisheries habitat restoration projects, CTUIR requires scalable field and remote monitoring tools to measure the results of these actions. This project will compare CHaMP field methodologies and PHaMS (see attachment) to compare measurements from remotely sensed and field data to address monitoring at these course scales.
        •      . . . . E.2.b.5 Habitat attribute studyY (Y/N)
          •      . . . . . . E.2.b.5.a
            Key issues addressed by habitat attribute research
            Patterns of stream temperature, geomorphic complexity, and the diversity and amount of riparian cover are among the most wide spread limiting factors or ecological conditions the inhibit the recovery of pacific salmon. Explicit consideration of spatial and temporal scale is necessary to create and track appropriate baseline conditions from the limiting factors/ecological conditions mentioned above (Beechie 2013).