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• 11. [Article] Threemile Creek Bull Trout Protection Final Report 1998

  Abstract -- Brook Trout were removed from Threemile Creek by electrofishing and night-snorkel spear-fishing. Electrofishing removal was conducted on 11 reaches and a total of 45 passes were completed. ...

  Citation × Citation Citation Abstract Copy Title: Threemile Creek Bull Trout Protection Final Report 1998 Abstract -- Brook Trout were removed from Threemile Creek by electrofishing and night-snorkel spear-fishing. Electrofishing removal was conducted on 11 reaches and a total of 45 passes were completed. Fifty brook trout were removed. Night-snorkeling was conducted in the five reach, intergrade zone where both bull and brook trout were found. Two comprehenzive passes were completed in the first three reaches, and three passes were completed in the last two reaches. A total of 10 brook trout and 8 brook/bull trout hybrids were removed. Additionally 39 brook trout were removed from a fire pond above Threemile Creek. Mollusk and amphibian surveys were also conducted; and temperature was collected in the Threemile Creek Project Area. Title: Threemile Creek Bull Trout Protection Final Report 1998 Abstract -- Brook Trout were removed from Threemile Creek by electrofishing and night-snorkel spear-fishing. Electrofishing removal was conducted on 11 reaches and a total of 45 passes were completed. Fifty brook trout were removed. Night-snorkeling was conducted in the five reach, intergrade zone where both bull and brook trout were found. Two comprehenzive passes were completed in the first three reaches, and three passes were completed in the last two reaches. A total of 10 brook trout and 8 brook/bull trout hybrids were removed. Additionally 39 brook trout were removed from a fire pond above Threemile Creek. Mollusk and amphibian surveys were also conducted; and temperature was collected in the Threemile Creek Project Area. Close

• 12. [Article] Riparian Function and Stream Temperature: Effectiveness of Oregon Department of Forestry’s Protection Rules and Strategies (OWEB #201-733)

  Abstract -- The Forest Practices Monitoring Program proposes in this report that future monitoring, with the objective to evaluate effectiveness, utilize a pre/post harvest measurement design coupled with ...

  Citation × Citation Citation Abstract Copy Title: Riparian Function and Stream Temperature: Effectiveness of Oregon Department of Forestry’s Protection Rules and Strategies (OWEB #201-733) Abstract -- The Forest Practices Monitoring Program proposes in this report that future monitoring, with the objective to evaluate effectiveness, utilize a pre/post harvest measurement design coupled with control reaches. The proposed project evaluates stream temperature and riparian condition before and after harvesting. Sites will be evaluated on both privately-owned and state-owed forestland. A pre/post- study design that establishes control, treatment, and downstream reaches, 2 years prior to harvest is proposed. Temperature, channel, overstory and understory riparian characteristics will be monitored two years prior to harvest and for 5 years after harvesting to evaluate harvest effects and recovery rates. This project approach, design, and proposed analysis will go through a review process involving reviewers from private research, DEQ, ODF&W, stakeholders, researchers, and representatives of the environmental caucuses. Title: Riparian Function and Stream Temperature: Effectiveness of Oregon Department of Forestry’s Protection Rules and Strategies (OWEB #201-733) Abstract -- The Forest Practices Monitoring Program proposes in this report that future monitoring, with the objective to evaluate effectiveness, utilize a pre/post harvest measurement design coupled with control reaches. The proposed project evaluates stream temperature and riparian condition before and after harvesting. Sites will be evaluated on both privately-owned and state-owed forestland. A pre/post- study design that establishes control, treatment, and downstream reaches, 2 years prior to harvest is proposed. Temperature, channel, overstory and understory riparian characteristics will be monitored two years prior to harvest and for 5 years after harvesting to evaluate harvest effects and recovery rates. This project approach, design, and proposed analysis will go through a review process involving reviewers from private research, DEQ, ODF&W, stakeholders, researchers, and representatives of the environmental caucuses. Close

• 13. [Article] Steelhead Habitat Surveys in Mill Creek Monitoring Project Completion Report (OWEB #205-125)

  Abstract -- This project added to the existing information about steelhead in Mill Creek in the following ways: • Oregon Department of Fish and Wildlife completed an instream habitat inventory from the ...

  Citation × Citation Citation Abstract Copy Title: Steelhead Habitat Surveys in Mill Creek Monitoring Project Completion Report (OWEB #205-125) Abstract -- This project added to the existing information about steelhead in Mill Creek in the following ways: • Oregon Department of Fish and Wildlife completed an instream habitat inventory from the mouth to the forks, up the South Fork to Mill Creek Falls, where anadromy ends, and up the North Fork for the first 7,370 meters. • Oregon Department of Fish and Wildlife conducted steelhead redd surveys in the mainstem and South Fork in 2005 and 2006, while the US Forest Service conducted redd surveys in the federally-owned upper reaches of the North Fork. • Wasco County Soil and Water Conservation District installed depth and temperature monitors on the mainstem and North Fork, while relying on the City of The Dalles to monitor flows in the South Fork. Title: Steelhead Habitat Surveys in Mill Creek Monitoring Project Completion Report (OWEB #205-125) Abstract -- This project added to the existing information about steelhead in Mill Creek in the following ways: • Oregon Department of Fish and Wildlife completed an instream habitat inventory from the mouth to the forks, up the South Fork to Mill Creek Falls, where anadromy ends, and up the North Fork for the first 7,370 meters. • Oregon Department of Fish and Wildlife conducted steelhead redd surveys in the mainstem and South Fork in 2005 and 2006, while the US Forest Service conducted redd surveys in the federally-owned upper reaches of the North Fork. • Wasco County Soil and Water Conservation District installed depth and temperature monitors on the mainstem and North Fork, while relying on the City of The Dalles to monitor flows in the South Fork. Close

• 14. [Article] Effectiveness Monitoring for LWD Placement in South Slough Tidal Wetlands (OWEB #205-111)

  Abstract -- Effectiveness monitoring of LWD placed in South Slough’s upper estuary wasdesigned to accomplish the following: - Determine presence/absence and behavior of juvenile salmonids (i.e., cohoand ...

  Citation × Citation Citation Abstract Copy Title: Effectiveness Monitoring for LWD Placement in South Slough Tidal Wetlands (OWEB #205-111) Abstract -- Effectiveness monitoring of LWD placed in South Slough’s upper estuary wasdesigned to accomplish the following: - Determine presence/absence and behavior of juvenile salmonids (i.e., cohoand cutthroat trout) in and around LWD using underwater videographyand acoustic tagging methods (a late addition to the project); - Monitor abundance and species composition of juvenile salmonids in tidal creeks with (and without) LWD using fyke nets; - Monitor fish use of other subtidal habitats with beach seines; - Track changes in invertebrate abundance and composition; - Detect wood movement with sub-meter GPS tracking; - Record changes in channel profile around LWD with detailed elevationsurveys; and, - Track water temperature and flow in locations near and away from LWD. Large woody debris was placed in 29 locations in South Slough’s upper estuary. The effectiveness monitoring project focused on 12 sites, six pairs based on configuration and location Title: Effectiveness Monitoring for LWD Placement in South Slough Tidal Wetlands (OWEB #205-111) Abstract -- Effectiveness monitoring of LWD placed in South Slough’s upper estuary wasdesigned to accomplish the following: - Determine presence/absence and behavior of juvenile salmonids (i.e., cohoand cutthroat trout) in and around LWD using underwater videographyand acoustic tagging methods (a late addition to the project); - Monitor abundance and species composition of juvenile salmonids in tidal creeks with (and without) LWD using fyke nets; - Monitor fish use of other subtidal habitats with beach seines; - Track changes in invertebrate abundance and composition; - Detect wood movement with sub-meter GPS tracking; - Record changes in channel profile around LWD with detailed elevationsurveys; and, - Track water temperature and flow in locations near and away from LWD. Large woody debris was placed in 29 locations in South Slough’s upper estuary. The effectiveness monitoring project focused on 12 sites, six pairs based on configuration and location Close

• 15. [Article] Little Deschutes Subbasin Watershed Assessment

  Abstract -- Many of the impacts to fish and wildlife habitat and water quality in the Little Deschutes River Subbasin are concentrated in the areas of housing, roads, and other human development. Most ...

  Citation × Citation Citation Abstract Copy Title: Little Deschutes Subbasin Watershed Assessment Abstract -- Many of the impacts to fish and wildlife habitat and water quality in the Little Deschutes River Subbasin are concentrated in the areas of housing, roads, and other human development. Most of the human population in the subbasin is concentrated around the community centers of La Pine, Gilchrist, Crescent, and Crescent Lake. There is significant dispersed development along the lower reaches of the Little Deschutes River between the communities of Sunriver and La Pine -an area characterized by gentle topography and depressions with forested wetlands, marshes and shallow lakes. Streams in this area, as illustrated by the Little Deschutes River , are low gradient and originate in the high elevation areas in the southwest portion of the watershed where there is higher precipitation. This ownership pattern has significant implications for natural resource management, as lower gradient floodplain areas tend to provide important wetland, fish, and wildlife habitat. Key Findings Fuel Loading: Having homes safe from wildfires is a concern for many residents. Fire suppression has increased the amount of dry wood in the area, creating a ready source for major wildfires. Riparian Areas and Wetlands: Loss of wetland and riparian areas , especially in the lower areas along the Little Deschutes River , has affected a number of resources. Water quality has been affected by the reduced wetlands that act as filters of nitrogen; the loss of streamside trees and other vegetation reduces shade that helps to cool water temperatures. Finally, loss ofwetlands and riparian vegetation has reduced important fish and wildlife habitats. Wildlife: The growth and development have altered wildlife habitats. Loss of wetlands, streamside vegetation, and other changes in the watershed have reduced important wildlife habitat. Roads and development have impacted migrating mule deer, increasing collisions between deer and cars and altering their migration pathways. Fish: There has been a significant loss of native trout and an increase in introduced brook and brown trout in the Little Deschutes River and tributaries. Loss of native trout is from competition with introduced species and changes in aquatic habitat and water temperatures. Water Quality: A major concern about the water in the river is unusually high temperatures in the summer and the abnormal growth of algae. Other studies indicated that there are problems with groundwater loading ofnitrogen. The high water table (with associated wetlands), and porous pumice soils contributes to increased nitrates, a by-product of septic systems and an indicator of human pathogens. Title: Little Deschutes Subbasin Watershed Assessment Abstract -- Many of the impacts to fish and wildlife habitat and water quality in the Little Deschutes River Subbasin are concentrated in the areas of housing, roads, and other human development. Most of the human population in the subbasin is concentrated around the community centers of La Pine, Gilchrist, Crescent, and Crescent Lake. There is significant dispersed development along the lower reaches of the Little Deschutes River between the communities of Sunriver and La Pine -an area characterized by gentle topography and depressions with forested wetlands, marshes and shallow lakes. Streams in this area, as illustrated by the Little Deschutes River , are low gradient and originate in the high elevation areas in the southwest portion of the watershed where there is higher precipitation. This ownership pattern has significant implications for natural resource management, as lower gradient floodplain areas tend to provide important wetland, fish, and wildlife habitat. Key Findings Fuel Loading: Having homes safe from wildfires is a concern for many residents. Fire suppression has increased the amount of dry wood in the area, creating a ready source for major wildfires. Riparian Areas and Wetlands: Loss of wetland and riparian areas , especially in the lower areas along the Little Deschutes River , has affected a number of resources. Water quality has been affected by the reduced wetlands that act as filters of nitrogen; the loss of streamside trees and other vegetation reduces shade that helps to cool water temperatures. Finally, loss ofwetlands and riparian vegetation has reduced important fish and wildlife habitats. Wildlife: The growth and development have altered wildlife habitats. Loss of wetlands, streamside vegetation, and other changes in the watershed have reduced important wildlife habitat. Roads and development have impacted migrating mule deer, increasing collisions between deer and cars and altering their migration pathways. Fish: There has been a significant loss of native trout and an increase in introduced brook and brown trout in the Little Deschutes River and tributaries. Loss of native trout is from competition with introduced species and changes in aquatic habitat and water temperatures. Water Quality: A major concern about the water in the river is unusually high temperatures in the summer and the abnormal growth of algae. Other studies indicated that there are problems with groundwater loading ofnitrogen. The high water table (with associated wetlands), and porous pumice soils contributes to increased nitrates, a by-product of septic systems and an indicator of human pathogens. Close

• 16. [Article] Upper Chewaucan Watershed Assessment

  Abstract -- Several assessment elements have good overall ratings and include the following: riparian vegetation/bank stability, Rosgen stream types, and pool numbers. However, the remaining elements need ...

  Citation × Citation Citation Abstract Copy Title: Upper Chewaucan Watershed Assessment Abstract -- Several assessment elements have good overall ratings and include the following: riparian vegetation/bank stability, Rosgen stream types, and pool numbers. However, the remaining elements need significant improvement to reach desired levels of high canopy coverage in forested sites, dense juniper woodlands, moderate road densities, lack of LWD, moderate to high stream temperatures, moderate to high spawning gravel fines, and culvert barriers. The less than desired conditions of these elements inhibit the Upper Chewaucan River Watershed from functioning appropriately as a redband trout reserve. As a result, this assessment element is functioning appropriately but-at-risk. Title: Upper Chewaucan Watershed Assessment Abstract -- Several assessment elements have good overall ratings and include the following: riparian vegetation/bank stability, Rosgen stream types, and pool numbers. However, the remaining elements need significant improvement to reach desired levels of high canopy coverage in forested sites, dense juniper woodlands, moderate road densities, lack of LWD, moderate to high stream temperatures, moderate to high spawning gravel fines, and culvert barriers. The less than desired conditions of these elements inhibit the Upper Chewaucan River Watershed from functioning appropriately as a redband trout reserve. As a result, this assessment element is functioning appropriately but-at-risk. Close

• 17. [Article] Salmonberry River Temperature Monitoring-STEP Project

  Abstract -- Results of a STEP project in which volunteers monitor summer temperatures in the Salmonberry River and tributaries. The project began collecting temperatures in 1994. Project history, protocol, ...

  Citation × Citation Citation Abstract Copy Title: Salmonberry River Temperature Monitoring-STEP Project Abstract -- Results of a STEP project in which volunteers monitor summer temperatures in the Salmonberry River and tributaries. The project began collecting temperatures in 1994. Project history, protocol, and results are summarized in pdf documents. Title: Salmonberry River Temperature Monitoring-STEP Project Abstract -- Results of a STEP project in which volunteers monitor summer temperatures in the Salmonberry River and tributaries. The project began collecting temperatures in 1994. Project history, protocol, and results are summarized in pdf documents. Close

• 18. [Article] CRTCP - Minimizing Risks and Mitigation of impacts to Bull Trout (Salvelinus confluentus) from Construction of Temperature Control Facilities at Cougar Reservoir, Oregon 2003

  Abstract -- Because drafting the reservoir may adversely affect bull trout, the Corps funded this study to minimize impacts of construction on bull trout. To protect this population, we need to more fully ...

  Citation × Citation Citation Abstract Copy Title: CRTCP - Minimizing Risks and Mitigation of impacts to Bull Trout (Salvelinus confluentus) from Construction of Temperature Control Facilities at Cougar Reservoir, Oregon 2003 Abstract -- Because drafting the reservoir may adversely affect bull trout, the Corps funded this study to minimize impacts of construction on bull trout. To protect this population, we need to more fully understand the movement and habitat use of bull trout in the South Fork McKenzie watershed, and to develop an emergency action plan should environmental conditions become detrimental to the overall health of the population. Recommendations from this project will be made to the Environmental Coordination Committee in the event that actions to protect bull trout become necessary. Title: CRTCP - Minimizing Risks and Mitigation of impacts to Bull Trout (Salvelinus confluentus) from Construction of Temperature Control Facilities at Cougar Reservoir, Oregon 2003 Abstract -- Because drafting the reservoir may adversely affect bull trout, the Corps funded this study to minimize impacts of construction on bull trout. To protect this population, we need to more fully understand the movement and habitat use of bull trout in the South Fork McKenzie watershed, and to develop an emergency action plan should environmental conditions become detrimental to the overall health of the population. Recommendations from this project will be made to the Environmental Coordination Committee in the event that actions to protect bull trout become necessary. Close

• 19. [Article] Tenmile Tributary Temperature Summary, 2008

  Abstract -- Continuous temperature monitoring for streams within the Tenmile Lakes basin. Including the following locations: Adams Creek (Middle Fork), Adams Creek (Right Fork), Johnson Creek (Swanson ...

  Citation × Citation Citation Abstract Copy Title: Tenmile Tributary Temperature Summary, 2008 Abstract -- Continuous temperature monitoring for streams within the Tenmile Lakes basin. Including the following locations: Adams Creek (Middle Fork), Adams Creek (Right Fork), Johnson Creek (Swanson Bridge #3), Johnson Creek Bridge, Johnson Delta, Roberts ESF, Roberts Creek (Lower), Benson ESF, Benson Creek Bridge, Alder Fork, Big Creek (Upper), Big Creek Dam Pool, Big Creek Bridge, Noble Creek (Upper), Noble Creek Bridge (Upper), Noble/Alder Bridge, Blacks Creek (Upper), Blacks Delta, Murphy Upper, and Murphy Lower Title: Tenmile Tributary Temperature Summary, 2008 Abstract -- Continuous temperature monitoring for streams within the Tenmile Lakes basin. Including the following locations: Adams Creek (Middle Fork), Adams Creek (Right Fork), Johnson Creek (Swanson Bridge #3), Johnson Creek Bridge, Johnson Delta, Roberts ESF, Roberts Creek (Lower), Benson ESF, Benson Creek Bridge, Alder Fork, Big Creek (Upper), Big Creek Dam Pool, Big Creek Bridge, Noble Creek (Upper), Noble Creek Bridge (Upper), Noble/Alder Bridge, Blacks Creek (Upper), Blacks Delta, Murphy Upper, and Murphy Lower Close

• 20. [Article] Tenmile Tributary Temperature Summary, 2009

  Abstract -- Continuous temperature monitoring for streams within the Tenmile Lakes basin. Including the following locations: Adams Creek (Upper Right Fork), Adams Creek (Lower Right Fork), Roberts Creek ...

  Citation × Citation Citation Abstract Copy Title: Tenmile Tributary Temperature Summary, 2009 Abstract -- Continuous temperature monitoring for streams within the Tenmile Lakes basin. Including the following locations: Adams Creek (Upper Right Fork), Adams Creek (Lower Right Fork), Roberts Creek ((Elliott State Forest (ESF)), Johnson Creek Bridge, Benson Creek ESF, Benson Creek Bridge, Benson Creek Delta, Alder Fork, Big Creek (Upper), Big Creek Dam Pool, Big Creek Bridge, Blacks Creek (Upper), Blacks Creek Delta, Murphy Creek (Upper). Title: Tenmile Tributary Temperature Summary, 2009 Abstract -- Continuous temperature monitoring for streams within the Tenmile Lakes basin. Including the following locations: Adams Creek (Upper Right Fork), Adams Creek (Lower Right Fork), Roberts Creek ((Elliott State Forest (ESF)), Johnson Creek Bridge, Benson Creek ESF, Benson Creek Bridge, Benson Creek Delta, Alder Fork, Big Creek (Upper), Big Creek Dam Pool, Big Creek Bridge, Blacks Creek (Upper), Blacks Creek Delta, Murphy Creek (Upper). Close