Cazadero North Stream Restoration Project

Salmonid Habitat Restoration and Acquisition

Fish Passage Improvement Instream Habitat Riparian Habitat
Project IDOWEB 220-8207-17281
Recovery DomainsWillamette River
Start Date12/01/2019
End Date03/13/2024
Year2019
StatusCompleted
Last Edited05/03/2024
 
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Description    


The Clackamas River Basin Council (CRBC) in close partnership with Metro (landowner), Clackamas County Department of Transportation & Development (County road interest) and Oregon Department of Fish and Wildlife together implemented the Cazadero North Stream Restoration Project (Project) on North Fork Deep Creek in Boring Oregon. Both instream, riparian and upland habitats have been degraded due to past land uses, road building and hydrologic changes within the watershed. CRBC and Metro restored instream and riparian habitats over a combined 3 acres of riparian area and 600 linear feet of stream by placing large wood, stabilizing a stormwater outfall, debris removal, riparian planting and invasive removal, placing stream bed cobbles/boulders and adding a concrete sill to the Richey Road culvert to improve fish passage with funding from OWEB, US Forest Service and Metro.

Project Benefit    


Clackamas River basin spring Chinook, coho and winter steelhead are negatively impacted by loss of habitat, impaired water quality and lack of access to historic spawning areas. This project will restore habitat elements believed to be most limiting to salmon and steelhead as identified in local and regional assessments referenced above and below in this application.

Lack of Large Wood: Only four pieces of large wood were noted within the active channel area of the project reach. Several more upland pieces were identified. A lack of mature conifers within the riparian and upland areas also limits future recruitment of large wood and its likely there is little to no recruitment area for large wood from upstream reaches given the configuration and dimensions of the Ritchey Road crossing. Large wood, especially key pieces are an important component of creating and maintaining physical habitat. Upland downed wood is also important for amphibians and other terrestrial species that require escape cover and areas for hibernation. Significantly increasing the density of large wood on the site would greatly enhance biological conditions for fish and wildlife.

Impaired Upstream Fish Passage: A preliminary evaluation of the SE Ritchey Road culvert crossing suggests that the culvert presents a depth barrier under low flow conditions and velocity barrier under high flow conditions. Although it would be difficult to improve high flow passage conditions without replacing the culvert with a more fish friendly approach, opportunities exist to improve fish passage at low flows with only slight modifications to the culvert.

Eroding storm water outfall: Outfall pipes, tributary head cuts and bank erosion associated with the energy dissipation from a storm water outfall have created areas of instability that contribute chronic sources of fine sediment to North Fork Deep Creek. Stabilization measures would be implemented at the outfall location to minimize erosion and protect water quality.

Lack of riparian vegetation: Removal of invasive plants and reestablishment of native trees and shrubs increases stream shade resulting in improved water quality. Additionally establishment of mature riparian vegetation creates long term sources of large wood.

Accomplishments

Metric Completed Originally
Proposed
Instream Habitat
  Stream Miles Treated .11 .11
Riparian Habitat
  Stream Miles Treated .22 .24
  Acres Treated 3.0 3.0
Fish Passage
  Barriers Removed
  Miles Opened .85 .85

Funding Details

SourceFunds
PCSRF$84,835
Other$176,305
In-Kind Donated Labor$7,680
Report Total:$268,820


Project Map



Worksites

20220124    


  • Worksite Identifier: 20220124
  • Start Date:
  • End Date:
Area Description

No Area Description data was found for this worksite.

Location Information

  • Basin:
  • Subbasin:
  • Watershed:
  • Subwatershed:
  • State: Oregon
  • Recovery Domain: Willamette River
  • Latitude: 45.42818702
  • Longitude: -122.37593266

ESU

  • Upper Willamette River Chinook Salmon ESU
  • Lower Columbia River Coho Salmon ESU
  • Lower Columbia River Steelhead DPS

Map

Photos

Metrics

Metrics
  • C.0 Salmonid Habitat Restoration and AcquisitionY (Y/N)
    •      . . C.0.a Habitat restoration and acquisition funding 268,819.90
    •      . . C.0.b Length of stream treated/protected .11
    •      . . C.0.c
      Project identified in a Plan or Watershed Assessment
      National Marine Fisheries Service Northwest Region, 2013-06-01, ESA Recovery Plan for Lower Columbia River Coho Salmon, Lower Columbia River Chinook Salmon, Columbia River Chum Salmon, and Lower Columbia River Steelhead; Oregon Department of Fish and Wildlife, 2016-01-01, Oregon Conservation Strategy ;
    •      . . C.0.d.1 Project Monitoring (LOV)
    •      . . C.0.d.2 Monitoring Location (LOV)
    •      . . C.2 Fish Passage ImprovementY (Y/N)
      •      . . . . C.2.a Fish Passage Funding 25,557.75
      •      . . . . C.2.b.1 Length of stream made accessible .85
      •      . . . . C.2.b.3 Type of blockage/barrier (LOV)
      •      . . . . C.2.b.4 Number of blockages/impediments/barriers impeding passage 1
      •      . . . . C.2.f.1 Culvert installed or improved at road stream crossingY (Y/N)
        •      . . . . . . C.2.f.2 Number of culverts installed or improved 1
        •      . . . . . . C.2.f.3 Miles of stream made accessible by culvert installation/upgrade .85
      •      . . C.4 Instream Habitat ProjectY (Y/N)
        •      . . . . C.4.a Instream Habitat Funding 229,510.97
        •      . . . . C.4.b Total length of instream habitat treated .11
        •      . . . . C.4.d.1 Channel structure placementY (Y/N)
          •      . . . . . . C.4.d.2 Material used for channel structure (LOV)
          •      . . . . . . C.4.d.3 Miles of stream treated through channel structure placement .11
          •      . . . . . . C.4.d.5 Pools expected to be created through channel structure placement 4
          •      . . . . . . C.4.d.7 Number of structures placed in channel 4
        •      . . . . C.4.e.1 Streambank stabilization Y (Y/N)
          •      . . . . . . C.4.e.2 Material Used For Streambank Stabilization (LOV)
          •      . . . . . . C.4.e.3 Miles of streambank stabilized .02
        •      . . C.5 Riparian Habitat ProjectY (Y/N)
          •      . . . . C.5.a Riparian Habitat Funding 5,913.07
          •      . . . . C.5.b.1 Total riparian miles streambank treated .22
          •      . . . . C.5.b.2 Total Riparian Acres Treated 3.0
          •      . . . . C.5.c.1 Riparian plantingY (Y/N)
            •      . . . . . . C.5.c.2
              Species of plants planted in riparian
              Western Red Cedar, Bigleaf Maple, Red Alder, Common snowberry, Pacific Ninebark, Red Osier Dogwood, Sitka Willow, Oceanspray, Tall Oregon Grape
            •      . . . . . . C.5.c.3 Acres planted in riparian 3.0
            •      . . . . . . C.5.c.4 Miles of streambank treated with riparian planting .22
          •      . . . . C.5.h.1 Riparian plant removal/controlY (Y/N)
            •      . . . . . . C.5.h.2
              Species of plants treated/removed in riparian
              Broadlead weeds including, blackberry, thistle, teasel, tansy, ivy and clematis.
            •      . . . . . . C.5.h.3 Acres of riparian treated for plant removal/control 3.0
            •      . . . . . . C.5.h.4 Miles of streambank treated for riparian plant removal/control .22
          •      . . . . C.5.j.1 Debris/structures removalY (Y/N)
            •      . . . . . . C.5.j.2 Acres of riparian treated for debris/structures removal 3.0
          •      . . C.11 Site maintenance projectY (Y/N)
            •      . . . . C.11.a Site maintenance funding 7,838.11
            •      . . . . C.11.b.1 Stream or streambank maintainedY (Y/N)
              •      . . . . . . C.11.b.2 Miles of streambank maintained .02