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• 71. [Article] 2000-2002, Effectiveness Monitoring for the Western Oregon Stream Restoration Program

  Abstract -- This report characterizes change in habitat conditions of restoration projects competed by Western Oregon Stream Restoration Program biologists. Typical restoration activities included the ...

  Citation × Citation Citation Abstract Copy Title: 2000-2002, Effectiveness Monitoring for the Western Oregon Stream Restoration Program Abstract -- This report characterizes change in habitat conditions of restoration projects competed by Western Oregon Stream Restoration Program biologists. Typical restoration activities included the placement of large wood and/or boulders in stream channels, removal of culvert passage barriers, riparian planting, road decommissioning, and streamside fencing. Implementation occurred coast-wide and in the Willamette Valley, with an overall goal of enhancing aquatic habitat for salmonid species. This program works in cooperation with the Oregon Heritage Foundation, Oregon Department of Forestry, US Fish and Wildlife Service, US Forest Service, industrial and private landowners, and watershed councils. Projects that were implemented in 2000 and 2001 were monitored to assess baseline pre-treatment and one-year post-treatment conditions. Additionally, projects that were treated in 1995 were monitored in 1996 to assess one-year post-treatment conditions and in 2001 to assess six-year posttreatment conditions. The objectives of the monitoring program were to describe changes in channel morphology, channel unit composition, and structural complexity in the restoration project areas. Title: 2000-2002, Effectiveness Monitoring for the Western Oregon Stream Restoration Program Abstract -- This report characterizes change in habitat conditions of restoration projects competed by Western Oregon Stream Restoration Program biologists. Typical restoration activities included the placement of large wood and/or boulders in stream channels, removal of culvert passage barriers, riparian planting, road decommissioning, and streamside fencing. Implementation occurred coast-wide and in the Willamette Valley, with an overall goal of enhancing aquatic habitat for salmonid species. This program works in cooperation with the Oregon Heritage Foundation, Oregon Department of Forestry, US Fish and Wildlife Service, US Forest Service, industrial and private landowners, and watershed councils. Projects that were implemented in 2000 and 2001 were monitored to assess baseline pre-treatment and one-year post-treatment conditions. Additionally, projects that were treated in 1995 were monitored in 1996 to assess one-year post-treatment conditions and in 2001 to assess six-year posttreatment conditions. The objectives of the monitoring program were to describe changes in channel morphology, channel unit composition, and structural complexity in the restoration project areas. Close

• 72. [Article] Spawning distribution and habitat use of adult Pacific and western brook lamprey in Smith River, Oregon Information Reports 2006-1

  Abstract -- Coastal Oregon populations of Pacific lamprey Lampetra tridentata and western brook lamprey L. richardsoni are considered depressed due to habitat loss and passage problems (Close et al. 2002, ...

  Citation × Citation Citation Abstract Copy Title: Spawning distribution and habitat use of adult Pacific and western brook lamprey in Smith River, Oregon Information Reports 2006-1 Abstract -- Coastal Oregon populations of Pacific lamprey Lampetra tridentata and western brook lamprey L. richardsoni are considered depressed due to habitat loss and passage problems (Close et al. 2002, Nawa 2003, ODFW 2006). Pacific lamprey was listed as an Oregon state sensitive species in 1993 and in 1996 was protected through restriction of harvest (ODFW 2006). Western brook lamprey is not protected and has no special state status. Abundance of Pacific lamprey throughout the coast and Columbia River has declined dramatically since the1960s. Dam counts at Winchester, Bonneville, and Leaburg dams show a dramatic decrease from historical levels (Kostow 2002, Nawa 2003, ODFW 2006). In 2003, eleven environmental groups petitioned the U.S. Fish and Wildlife Service to list Pacific, western brook, and two other lamprey species as endangered in the Pacific Northwest and California (Nawa 2003). Even though the petition cited habitat losses due to reduced in-stream flows, water diversions, dredging, scour and channnelization issues, pollution and degradation of riparian communities, the U.S. Fish and Wildlife Service determined the petition did not contain adequate information to warrant a listing (Federal Register, 69 (27 December 2004) 77158-77167). The Oregon Department of Fish and Wildlife recently reviewed the status of western brook and Pacific lamprey and found populations to be ‘at risk’ of extinction (ODFW 2006) due to habitat loss, passage barriers and pollution. However data necessary to conduct a thorough and detailed assessment are lacking. Much of the data lacking are critical to the effective management and conservation of Oregon’s coastal lamprey species. The Columbia River Basin Lamprey Technical Workgroup (CRBLTW 2005) and members of Columbia River Inter-Tribal Fish Commission (CRITFC 2004) have identified and prioritized critical data gaps for Pacific lamprey, many of which also apply to western brook lamprey. Among these are 1) methods to assess distribution and abundance of all life stages and appropriate techniques for monitoring population status; 2) population structure and delineation; 3) population dynamics; 4) basic biology including interspecific and community level relationships; 5) limiting factors and threats including passage issues, and 6) habitat needs and requirements. This study addresses information needs pertaining to distribution and habitat use in addition to providing basic descriptive ecology. Our goal was to identify habitat variables associated with spawning Pacific and western brook lamprey in order to infer distribution throughout coastal Oregon. The objectives of this study were to 1) determine distribution of spawning Pacific and western brook lamprey in the Smith River basin; 2) describe redds of both species; and 3) describe associations of spawning Pacific and western brook lamprey in relation to habitat unit and reach scale habitat characteristics. Title: Spawning distribution and habitat use of adult Pacific and western brook lamprey in Smith River, Oregon Information Reports 2006-1 Abstract -- Coastal Oregon populations of Pacific lamprey Lampetra tridentata and western brook lamprey L. richardsoni are considered depressed due to habitat loss and passage problems (Close et al. 2002, Nawa 2003, ODFW 2006). Pacific lamprey was listed as an Oregon state sensitive species in 1993 and in 1996 was protected through restriction of harvest (ODFW 2006). Western brook lamprey is not protected and has no special state status. Abundance of Pacific lamprey throughout the coast and Columbia River has declined dramatically since the1960s. Dam counts at Winchester, Bonneville, and Leaburg dams show a dramatic decrease from historical levels (Kostow 2002, Nawa 2003, ODFW 2006). In 2003, eleven environmental groups petitioned the U.S. Fish and Wildlife Service to list Pacific, western brook, and two other lamprey species as endangered in the Pacific Northwest and California (Nawa 2003). Even though the petition cited habitat losses due to reduced in-stream flows, water diversions, dredging, scour and channnelization issues, pollution and degradation of riparian communities, the U.S. Fish and Wildlife Service determined the petition did not contain adequate information to warrant a listing (Federal Register, 69 (27 December 2004) 77158-77167). The Oregon Department of Fish and Wildlife recently reviewed the status of western brook and Pacific lamprey and found populations to be ‘at risk’ of extinction (ODFW 2006) due to habitat loss, passage barriers and pollution. However data necessary to conduct a thorough and detailed assessment are lacking. Much of the data lacking are critical to the effective management and conservation of Oregon’s coastal lamprey species. The Columbia River Basin Lamprey Technical Workgroup (CRBLTW 2005) and members of Columbia River Inter-Tribal Fish Commission (CRITFC 2004) have identified and prioritized critical data gaps for Pacific lamprey, many of which also apply to western brook lamprey. Among these are 1) methods to assess distribution and abundance of all life stages and appropriate techniques for monitoring population status; 2) population structure and delineation; 3) population dynamics; 4) basic biology including interspecific and community level relationships; 5) limiting factors and threats including passage issues, and 6) habitat needs and requirements. This study addresses information needs pertaining to distribution and habitat use in addition to providing basic descriptive ecology. Our goal was to identify habitat variables associated with spawning Pacific and western brook lamprey in order to infer distribution throughout coastal Oregon. The objectives of this study were to 1) determine distribution of spawning Pacific and western brook lamprey in the Smith River basin; 2) describe redds of both species; and 3) describe associations of spawning Pacific and western brook lamprey in relation to habitat unit and reach scale habitat characteristics. Close

• 73. [Article] Clear and Foster Creek Watershed Assessment

  Abstract -- A watershed assessment was completed in the Clear and Foster Creek watersheds to evaluate existing conditions and make recommendations to protect or enhance watershed natural resources. Clear ...

  Citation × Citation Citation Abstract Copy Title: Clear and Foster Creek Watershed Assessment Abstract -- A watershed assessment was completed in the Clear and Foster Creek watersheds to evaluate existing conditions and make recommendations to protect or enhance watershed natural resources. Clear and Foster Creek are tributaries to the Clackamas River below any major dams on the system; consequently these tributaries are positioned favorably to contribute to recovery of important anadromous fish populations. Anadromous fish species in the Clackamas basin include spring and fall chinook, coho salmon, winter steelhead, summer steelhead (non-native), migratory cutthroat trout and lamprey. Clear and Foster Creeks are utilized by fall chinook, winter steelhead and coho salmon. The assessment generally followed the framework described in the Oregon Watershed Enhancement Board’s Watershed Assessment Manual (WPN, 1999). The assessment focused on the following components: Channel habitat classification and modification; hydrology and water use; riparian/wetlands; sediment sources; water quality; fisheries; and wildlife and upland vegetation. Generally the approach builds on existing information, and enhances this information with aerial photo interpretation and limited field checking. Additional fieldwork was used to verify channel habitat types and to characterize fish habitat condition. GIS was used as a critical assessment tool and method of displaying results. Title: Clear and Foster Creek Watershed Assessment Abstract -- A watershed assessment was completed in the Clear and Foster Creek watersheds to evaluate existing conditions and make recommendations to protect or enhance watershed natural resources. Clear and Foster Creek are tributaries to the Clackamas River below any major dams on the system; consequently these tributaries are positioned favorably to contribute to recovery of important anadromous fish populations. Anadromous fish species in the Clackamas basin include spring and fall chinook, coho salmon, winter steelhead, summer steelhead (non-native), migratory cutthroat trout and lamprey. Clear and Foster Creeks are utilized by fall chinook, winter steelhead and coho salmon. The assessment generally followed the framework described in the Oregon Watershed Enhancement Board’s Watershed Assessment Manual (WPN, 1999). The assessment focused on the following components: Channel habitat classification and modification; hydrology and water use; riparian/wetlands; sediment sources; water quality; fisheries; and wildlife and upland vegetation. Generally the approach builds on existing information, and enhances this information with aerial photo interpretation and limited field checking. Additional fieldwork was used to verify channel habitat types and to characterize fish habitat condition. GIS was used as a critical assessment tool and method of displaying results. Close

• 74. [Article] Phillips Creek Watershed Assessment

  Abstract -- Watershed Assessments for the Grande Ronde River Subwatersheds are being prepared for the Grande Ronde Model Watershed Program. This Watershed Assessment addresses the Phillips Creek Watershed ...

  Citation × Citation Citation Abstract Copy Title: Phillips Creek Watershed Assessment Abstract -- Watershed Assessments for the Grande Ronde River Subwatersheds are being prepared for the Grande Ronde Model Watershed Program. This Watershed Assessment addresses the Phillips Creek Watershed located near Elgin, Oregon. Phillips Creek is a relatively small watershed (4th order HUC – Hydrologic Unit Classification) containing about 33 square miles or slightly over 24,000 acres. Phillips Creek empties into the Grande Ronde River in Elgin. It is an intermittent stream in some reaches, but water flows year around in other reaches. In this Assessment the main emphasis is on the nonfederal lands. The USDA Forest Service – Umatilla National Forest recently completed a watershed assessment on the National Forest area that includes Phillips, Cabin, Gordon and Dry Creeks. For more complete information on watershed condition on federal lands, please refer to the Umatilla National Forest’s Phillips-Gordon Ecosystem Analysis (PGEA). This assessment will describe the Phillips Creek watershed and help to identify the stream processes and features that are working well, and those that are not. Information that is already available from state and federal agencies as well as from private sources (including people that live in the area) will be used. Several public meetings were held to obtain information and insights from people that live in the area. The assessment will identify human’s positive and negative influences to the immediate stream environment. The assessment should provide enough information to develop project plans and monitoring plans that will help to protect and improve water quality and fish habitat in Phillips Creek and its tributaries. This assessment includes a description of Phillips Creek Watershed, historical conditions assessment, channel habitat type classification, hydrology and water use, riparian assessment, wetlands assessment, sediment sources assessment, channel modification assessment, water quality assessment, water rights assessment, fish and fish habitat assessment, upland conditions assessment – Forest, upland conditions assessment – Range, developed area assessment, noxious weeds assessment, and a watershed condition evaluation. Title: Phillips Creek Watershed Assessment Abstract -- Watershed Assessments for the Grande Ronde River Subwatersheds are being prepared for the Grande Ronde Model Watershed Program. This Watershed Assessment addresses the Phillips Creek Watershed located near Elgin, Oregon. Phillips Creek is a relatively small watershed (4th order HUC – Hydrologic Unit Classification) containing about 33 square miles or slightly over 24,000 acres. Phillips Creek empties into the Grande Ronde River in Elgin. It is an intermittent stream in some reaches, but water flows year around in other reaches. In this Assessment the main emphasis is on the nonfederal lands. The USDA Forest Service – Umatilla National Forest recently completed a watershed assessment on the National Forest area that includes Phillips, Cabin, Gordon and Dry Creeks. For more complete information on watershed condition on federal lands, please refer to the Umatilla National Forest’s Phillips-Gordon Ecosystem Analysis (PGEA). This assessment will describe the Phillips Creek watershed and help to identify the stream processes and features that are working well, and those that are not. Information that is already available from state and federal agencies as well as from private sources (including people that live in the area) will be used. Several public meetings were held to obtain information and insights from people that live in the area. The assessment will identify human’s positive and negative influences to the immediate stream environment. The assessment should provide enough information to develop project plans and monitoring plans that will help to protect and improve water quality and fish habitat in Phillips Creek and its tributaries. This assessment includes a description of Phillips Creek Watershed, historical conditions assessment, channel habitat type classification, hydrology and water use, riparian assessment, wetlands assessment, sediment sources assessment, channel modification assessment, water quality assessment, water rights assessment, fish and fish habitat assessment, upland conditions assessment – Forest, upland conditions assessment – Range, developed area assessment, noxious weeds assessment, and a watershed condition evaluation. Close

• 75. [Article] Pine Hollow - Jackknife Creek Watershed Assessment

  Abstract -- The assessment area is located in north-central Oregon within the semi-arid Columbia Plateau and the Lower John Day River Basin. The assessment area occupies the southeastern portion of Sherman ...

  Citation × Citation Citation Abstract Copy Title: Pine Hollow - Jackknife Creek Watershed Assessment Abstract -- The assessment area is located in north-central Oregon within the semi-arid Columbia Plateau and the Lower John Day River Basin. The assessment area occupies the southeastern portion of Sherman County and part of the northeastern portion of Wasco County, beginning southeast of the town of Grass Valley and including the towns of Kent and Shaniko. The watershed assessment area is sparsely populated, with an average population density of less than one person per square mile in Sherman County and two per square mile in Wasco County (U.S. Census Bureau 2010). All of the streams within the Pine Hollow – Jackknife Creek watershed assessment area drain into the Lower John Day River, and the river is the eastern border of the assessment area. The 8,000 square mile John Day Basin is the fourth largest basin in the state. The main stem of the John Day River originates in the Blue Mountains southeast of Prairie City, Oregon, and flows generally westward then northward for approximately 284 miles before discharging into the Columbia River at River Mile (RM) 218, just east of the town of Rufus, Oregon. Title: Pine Hollow - Jackknife Creek Watershed Assessment Abstract -- The assessment area is located in north-central Oregon within the semi-arid Columbia Plateau and the Lower John Day River Basin. The assessment area occupies the southeastern portion of Sherman County and part of the northeastern portion of Wasco County, beginning southeast of the town of Grass Valley and including the towns of Kent and Shaniko. The watershed assessment area is sparsely populated, with an average population density of less than one person per square mile in Sherman County and two per square mile in Wasco County (U.S. Census Bureau 2010). All of the streams within the Pine Hollow – Jackknife Creek watershed assessment area drain into the Lower John Day River, and the river is the eastern border of the assessment area. The 8,000 square mile John Day Basin is the fourth largest basin in the state. The main stem of the John Day River originates in the Blue Mountains southeast of Prairie City, Oregon, and flows generally westward then northward for approximately 284 miles before discharging into the Columbia River at River Mile (RM) 218, just east of the town of Rufus, Oregon. Close

• 76. [Article] Effectiveness Monitoring Report for the Western Oregon Stream Restoration Program, 1999-2008 Report Number: OPSW-ODFW-2010-6

  Abstract -- State and federal agencies have invested millions of dollars to restore streams and watersheds in the Pacific Northwest over the past two decades. In Oregon alone, over 500 million dollars ...

  Citation × Citation Citation Abstract Copy Title: Effectiveness Monitoring Report for the Western Oregon Stream Restoration Program, 1999-2008 Report Number: OPSW-ODFW-2010-6 Abstract -- State and federal agencies have invested millions of dollars to restore streams and watersheds in the Pacific Northwest over the past two decades. In Oregon alone, over 500 million dollars has been spent on completed projects from 1995 to 2007 (Oregon Watershed Enhancement Board 2009). Restoration practitioners have distributed the investment among watershed scale activities such as road repair, dam removal, and upland management, and stream scale activities such as passage, instream complexity, and riparian plantings. The Western Oregon Stream Restoration Program (WOSRP) was established to work in cooperation with private and corporate landowners to restore stream habitat for juvenile and adult salmonids. In addition to the WOSRP, the Oregon Watershed Enhancement Board (OWEB) funds restoration projects with local watershed councils, who commonly partner with state and federal agencies. Eight WOSRP restoration biologists in Tillamook, Newport, Charleston, Gold Beach, Roseburg, Clackamas, and Salem select sites and implement projects consistent with the criteria described in Thom et al (2001). A monitoring component is integrated in the program, with surveys coordinated and reported by a biologist in Corvallis. The goal of the monitoring program is to assess the long term effectiveness of instream restoration projects implemented by WOSRP, and to evaluate progress towards salmon conservation and recovery goals in Oregon’s coastal basins. The WOSRP restoration sites are distributed throughout the Willamette, Lower Columbia, and coastal drainage's. Restoration treatments added large wood and/or boulders, improved fish passage, planted trees in riparian areas, or were a combination of the three. Large wood was placed in complex jams at intervals throughout the stream to increase stream roughness and complexity. Boulders were sometimes used in conjunction with wood jams to provide stability to the structures, and prevent large wood from moving downstream and posing a hazard to culverts and bridges. Bedrock dominated streams were often treated with boulders to collect gravel and cobble, intended to aggrade the streambed. In the future, large wood may be added to these streams. Fish passage projects opened previously inaccessible habitat to juvenile and/or adult salmonids while riparian plantings and fencing were designed to improve riparian vegetation and bank structure. The project length varied from site to site. Fish passage sites were quite short, but provided access to kilometers of fish habitat, and large wood sites were up to several kilometers in length. Large wood and boulder placement projects have become commonplace in the Pacific Northwest to restore complex stream habitat for juvenile coho and other salmonids (Katz et al. 2007, Roni et al. 2008). Detailed assessments have been published for individual projects or experiments (e.g. Moore and Gregory, 1988, Nickelson et al. 1992, Cederholm et al.1997). More extensive evaluations have used a post treatment design (Hicks et al 1991, Roni and Quinn 2001), but none have used a pre- and post treatment design. In this paper we evaluate habitat changes at 103 restoration projects in western Oregon from pre-treatment to one year post treatment to 6 years following treatment. Projects commonly treated 0.5 – 1 km of stream, but some extended up to 6 km. The projects we evaluated in this paper were treated with large logs, usually arranged in jams, and were not cabled or driven into banks or bottom. As of 2008, the OWEB and WOSRP projects have treated approximately 750 km of stream with large wood (Figure 1), 120 km with boulders, and over 4,000 km of stream have been made accessible by replacing and/or removing culverts. Each year, OWEB receives 210 grant applications for restoration projects. These projects generally adhere to a similar selection process and design, so the results of this study can be expected to apply more broadly within the Pacific Northwest. Roni et al (2008), in a synthesis paper, summarized many of the potential physical benefits of restoration; these include pool depth and frequency, habitat complexity, woody debris, and sediment retention and quality of spawning gravel. Some projects in deeply incised channels have reduced the incision and increased bed elevation. Evaluations of biological responses have been confounded by natural variability of populations, duration of study, or length of stream examined. For example, determination of success based on spawning ground counts is problematic because of variation in ocean survival. However, longer duration and watershed scale studies have shown positive responses of juvenile and adult salmon (Johnson et al 2005). Burnett et al. (2008) conducted a systematic review of peer-reviewed articles to examine the effects of large wood placement on salmonid abundance, growth, or survival, or on overall stream habitat complexity. Few publications were both relevant and met the rigorous standards outlined in their review. Although the review supported short term improvements in habitat complexity, the relationship to salmonid productivity was less definitive. Notable exceptions included Johnson et al. (2005) cited above, and Solazzi et al. (2000). An alternative approach to directly assessing biological response is to model potential changes in abundance or productivity. The Habitat Limiting Factors Model (Reeves et al. 1989, Nickelson et al.1992a, Nickelson 1998) was developed to quantify the carrying capacity of coastal streams for juvenile coho during the summer and winter. Use of this model is appropriate because most of the instream restoration projects in western Oregon were intended to improve habitat for juvenile coho. In this paper, we evaluated the physical response directly, and quantified the potential response of juvenile coho salmon by application of the Habitat Limiting Factors Model. Project effectiveness monitoring requires linking the restoration treatment to improved physical conditions for and biological response of salmon (Katz et al. 2007) and defining desired outcomes (Rumps et al. 2007). Because the WOSRP projects were designed to improve ecological and hydrologic stream function specifically for salmonids, we evaluated 1) retention of wood structures, 2) natural recruitment of additional wood, 3) increase in pool number, area, and depth, 4) retention of gravels and sorting of finer substrates, and 5) increase in channel complexity – secondary channels and off-channel habitats. Biological evaluation was based on estimates of the potential carrying capacity for juvenile coho during the overwinter life stage. The primary objectives of this evaluation are to test for these changes one year following treatment and 6 years following treatment. Secondarily, we evaluated the response of the projects by geographic location and position along the stream network. Previous WOSRP monitoring reports (e.g. Jacobsen and Jones 2003, Jacobsen et al. 2007) have focused on conditions one year following treatment, with relatively few sites assessed 2-3 years following restoration. Since 2003, the restoration projects have increased in complexity – more and larger pieces and jams, and treated more kilometers of stream length per site. The WOSRP program has provided a unique opportunity to evaluate the effects of restoration projects over longer times and broader geographic scales than previously feasible. We have been surveying the restoration sites in both summer and winter to monitor changes in stream habitat and evaluate the success of treatments, such as the placement of wood and/or boulders and fish passage. Surveys are logistically easier to manage in the summer, but surveys conducted during the winter provide a more timely and accurate assessment of over-winter rearing potential for juvenile coho. Because we have paired surveys, we are able to assess the added value of revisits across seasons. We test the hypothesis that habitat characteristics at the restoration sites do not change from summer to winter. The findings permit us to modify the survey program if the information is duplicative, and use the resources in another fashion. Title: Effectiveness Monitoring Report for the Western Oregon Stream Restoration Program, 1999-2008 Report Number: OPSW-ODFW-2010-6 Abstract -- State and federal agencies have invested millions of dollars to restore streams and watersheds in the Pacific Northwest over the past two decades. In Oregon alone, over 500 million dollars has been spent on completed projects from 1995 to 2007 (Oregon Watershed Enhancement Board 2009). Restoration practitioners have distributed the investment among watershed scale activities such as road repair, dam removal, and upland management, and stream scale activities such as passage, instream complexity, and riparian plantings. The Western Oregon Stream Restoration Program (WOSRP) was established to work in cooperation with private and corporate landowners to restore stream habitat for juvenile and adult salmonids. In addition to the WOSRP, the Oregon Watershed Enhancement Board (OWEB) funds restoration projects with local watershed councils, who commonly partner with state and federal agencies. Eight WOSRP restoration biologists in Tillamook, Newport, Charleston, Gold Beach, Roseburg, Clackamas, and Salem select sites and implement projects consistent with the criteria described in Thom et al (2001). A monitoring component is integrated in the program, with surveys coordinated and reported by a biologist in Corvallis. The goal of the monitoring program is to assess the long term effectiveness of instream restoration projects implemented by WOSRP, and to evaluate progress towards salmon conservation and recovery goals in Oregon’s coastal basins. The WOSRP restoration sites are distributed throughout the Willamette, Lower Columbia, and coastal drainage's. Restoration treatments added large wood and/or boulders, improved fish passage, planted trees in riparian areas, or were a combination of the three. Large wood was placed in complex jams at intervals throughout the stream to increase stream roughness and complexity. Boulders were sometimes used in conjunction with wood jams to provide stability to the structures, and prevent large wood from moving downstream and posing a hazard to culverts and bridges. Bedrock dominated streams were often treated with boulders to collect gravel and cobble, intended to aggrade the streambed. In the future, large wood may be added to these streams. Fish passage projects opened previously inaccessible habitat to juvenile and/or adult salmonids while riparian plantings and fencing were designed to improve riparian vegetation and bank structure. The project length varied from site to site. Fish passage sites were quite short, but provided access to kilometers of fish habitat, and large wood sites were up to several kilometers in length. Large wood and boulder placement projects have become commonplace in the Pacific Northwest to restore complex stream habitat for juvenile coho and other salmonids (Katz et al. 2007, Roni et al. 2008). Detailed assessments have been published for individual projects or experiments (e.g. Moore and Gregory, 1988, Nickelson et al. 1992, Cederholm et al.1997). More extensive evaluations have used a post treatment design (Hicks et al 1991, Roni and Quinn 2001), but none have used a pre- and post treatment design. In this paper we evaluate habitat changes at 103 restoration projects in western Oregon from pre-treatment to one year post treatment to 6 years following treatment. Projects commonly treated 0.5 – 1 km of stream, but some extended up to 6 km. The projects we evaluated in this paper were treated with large logs, usually arranged in jams, and were not cabled or driven into banks or bottom. As of 2008, the OWEB and WOSRP projects have treated approximately 750 km of stream with large wood (Figure 1), 120 km with boulders, and over 4,000 km of stream have been made accessible by replacing and/or removing culverts. Each year, OWEB receives 210 grant applications for restoration projects. These projects generally adhere to a similar selection process and design, so the results of this study can be expected to apply more broadly within the Pacific Northwest. Roni et al (2008), in a synthesis paper, summarized many of the potential physical benefits of restoration; these include pool depth and frequency, habitat complexity, woody debris, and sediment retention and quality of spawning gravel. Some projects in deeply incised channels have reduced the incision and increased bed elevation. Evaluations of biological responses have been confounded by natural variability of populations, duration of study, or length of stream examined. For example, determination of success based on spawning ground counts is problematic because of variation in ocean survival. However, longer duration and watershed scale studies have shown positive responses of juvenile and adult salmon (Johnson et al 2005). Burnett et al. (2008) conducted a systematic review of peer-reviewed articles to examine the effects of large wood placement on salmonid abundance, growth, or survival, or on overall stream habitat complexity. Few publications were both relevant and met the rigorous standards outlined in their review. Although the review supported short term improvements in habitat complexity, the relationship to salmonid productivity was less definitive. Notable exceptions included Johnson et al. (2005) cited above, and Solazzi et al. (2000). An alternative approach to directly assessing biological response is to model potential changes in abundance or productivity. The Habitat Limiting Factors Model (Reeves et al. 1989, Nickelson et al.1992a, Nickelson 1998) was developed to quantify the carrying capacity of coastal streams for juvenile coho during the summer and winter. Use of this model is appropriate because most of the instream restoration projects in western Oregon were intended to improve habitat for juvenile coho. In this paper, we evaluated the physical response directly, and quantified the potential response of juvenile coho salmon by application of the Habitat Limiting Factors Model. Project effectiveness monitoring requires linking the restoration treatment to improved physical conditions for and biological response of salmon (Katz et al. 2007) and defining desired outcomes (Rumps et al. 2007). Because the WOSRP projects were designed to improve ecological and hydrologic stream function specifically for salmonids, we evaluated 1) retention of wood structures, 2) natural recruitment of additional wood, 3) increase in pool number, area, and depth, 4) retention of gravels and sorting of finer substrates, and 5) increase in channel complexity – secondary channels and off-channel habitats. Biological evaluation was based on estimates of the potential carrying capacity for juvenile coho during the overwinter life stage. The primary objectives of this evaluation are to test for these changes one year following treatment and 6 years following treatment. Secondarily, we evaluated the response of the projects by geographic location and position along the stream network. Previous WOSRP monitoring reports (e.g. Jacobsen and Jones 2003, Jacobsen et al. 2007) have focused on conditions one year following treatment, with relatively few sites assessed 2-3 years following restoration. Since 2003, the restoration projects have increased in complexity – more and larger pieces and jams, and treated more kilometers of stream length per site. The WOSRP program has provided a unique opportunity to evaluate the effects of restoration projects over longer times and broader geographic scales than previously feasible. We have been surveying the restoration sites in both summer and winter to monitor changes in stream habitat and evaluate the success of treatments, such as the placement of wood and/or boulders and fish passage. Surveys are logistically easier to manage in the summer, but surveys conducted during the winter provide a more timely and accurate assessment of over-winter rearing potential for juvenile coho. Because we have paired surveys, we are able to assess the added value of revisits across seasons. We test the hypothesis that habitat characteristics at the restoration sites do not change from summer to winter. The findings permit us to modify the survey program if the information is duplicative, and use the resources in another fashion. Close

• 77. [Article] Vector Control - Wetlands of Concern

  Abstract -- The Wetlands of Concern dataset represents one type of “sensitive area” for the purpose of reviewing and approving Pesticide Use Plans per ODFW's obligations under ORS 452.140 and ORS 452.245. ...

  Citation × Citation Citation Abstract Copy Title: Vector Control - Wetlands of Concern Abstract -- The Wetlands of Concern dataset represents one type of “sensitive area” for the purpose of reviewing and approving Pesticide Use Plans per ODFW's obligations under ORS 452.140 and ORS 452.245. ODFW will only make recommendations for mosquito control treatment protocols on sensitive areas, as identified in ODFW's Vector Control Guidance for Sensitive Areas (http://www.dfw.state.or.us/fish/water/docs/Sensitive_Area_Guidance.pdf) or confirmed by the local fish and wildlife biologists utilizing the guidelines in the document. In general, a sensitive area is any area where fish and wildlife and their habitats are rare or of local importance due to their special nature or role in the ecosystem. Species-specific and location-specific details are not maintained in this dataset. This dataset is derived from the Oregon Wetlands Cover. The Oregon Wetlands Cover is a key component of the Oregon Wetland Explorer data portal (http://oregonexplorer.info/wetlands), and is intended to (1) serve as a framework for storing and disseminating information on the state's wetlands, and (2) promote comprehensive monitoring, assessment, conservation, and restoration of Oregon's wetlands. Wetlands with a Total Conservation Significance score of 70 and above were included in this dataset for the purpose of identifying wetlands of concern for vector control purposes. Title: Vector Control - Wetlands of Concern Abstract -- The Wetlands of Concern dataset represents one type of “sensitive area” for the purpose of reviewing and approving Pesticide Use Plans per ODFW's obligations under ORS 452.140 and ORS 452.245. ODFW will only make recommendations for mosquito control treatment protocols on sensitive areas, as identified in ODFW's Vector Control Guidance for Sensitive Areas (http://www.dfw.state.or.us/fish/water/docs/Sensitive_Area_Guidance.pdf) or confirmed by the local fish and wildlife biologists utilizing the guidelines in the document. In general, a sensitive area is any area where fish and wildlife and their habitats are rare or of local importance due to their special nature or role in the ecosystem. Species-specific and location-specific details are not maintained in this dataset. This dataset is derived from the Oregon Wetlands Cover. The Oregon Wetlands Cover is a key component of the Oregon Wetland Explorer data portal (http://oregonexplorer.info/wetlands), and is intended to (1) serve as a framework for storing and disseminating information on the state's wetlands, and (2) promote comprehensive monitoring, assessment, conservation, and restoration of Oregon's wetlands. Wetlands with a Total Conservation Significance score of 70 and above were included in this dataset for the purpose of identifying wetlands of concern for vector control purposes. Close

• 78. [Article] Fish Management Plan Yachats River, 1979

  Abstract -- The Yachats River is a moderate-sized tributary to the Pacific Ocean containing 55 stream miles and a small estuary. This is an excellent small system that is not stocked with hatchery fish ...

  Citation × Citation Citation Abstract Copy Title: Fish Management Plan Yachats River, 1979 Abstract -- The Yachats River is a moderate-sized tributary to the Pacific Ocean containing 55 stream miles and a small estuary. This is an excellent small system that is not stocked with hatchery fish since the habitat is capable of producing a good population of wild fish. The stream receives light angling pressure; but we believe this will increase and more restrictive angling regulations may eventually be needed, although none are necessary now. The Yachats produces resident and anadromous cutthroat trout, fall Chinook and coho salmon, and winter steelhead. Releases of hatchery steelhead were terminated in 1969; cutthroat trout in 1978; and the only known release of salmon was made in 1958. There are no special angling regulations in effect at present. Maintenance of water quality, summertime streamflows, riparian vegetation, and prevention of stream channel alterations are key elements in protecting the capability of this stream to sustain natural production of al] salmonids. In July 1979, the Oregon Fish and Wildlife Commission accepted the following Department recommendations: The Yachats River will be managed for wild trout. The Yachats River will be managed for wild steelhead for the immediate future. However, if ODFW determines that steelheaders are opposed to this option, the Fish and Wildlife Commission will consider authorizing the release of hatchery smolts to enhance the fishery. The choice of a management option for salmon will be deferred until a coast-wide salmon management plan is developed. At that time, staff biologists will decide on a final recommendation to the Fish and Wildlife Commission regarding the need or desirability for releasing hatchery salmon into the system. Title: Fish Management Plan Yachats River, 1979 Abstract -- The Yachats River is a moderate-sized tributary to the Pacific Ocean containing 55 stream miles and a small estuary. This is an excellent small system that is not stocked with hatchery fish since the habitat is capable of producing a good population of wild fish. The stream receives light angling pressure; but we believe this will increase and more restrictive angling regulations may eventually be needed, although none are necessary now. The Yachats produces resident and anadromous cutthroat trout, fall Chinook and coho salmon, and winter steelhead. Releases of hatchery steelhead were terminated in 1969; cutthroat trout in 1978; and the only known release of salmon was made in 1958. There are no special angling regulations in effect at present. Maintenance of water quality, summertime streamflows, riparian vegetation, and prevention of stream channel alterations are key elements in protecting the capability of this stream to sustain natural production of al] salmonids. In July 1979, the Oregon Fish and Wildlife Commission accepted the following Department recommendations: The Yachats River will be managed for wild trout. The Yachats River will be managed for wild steelhead for the immediate future. However, if ODFW determines that steelheaders are opposed to this option, the Fish and Wildlife Commission will consider authorizing the release of hatchery smolts to enhance the fishery. The choice of a management option for salmon will be deferred until a coast-wide salmon management plan is developed. At that time, staff biologists will decide on a final recommendation to the Fish and Wildlife Commission regarding the need or desirability for releasing hatchery salmon into the system. Close