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• 1831. [Article] Sandy River Basin Fish Management Plan 1997 Draft

  Abstract -- The Sandy River and its tributaries originate high on the west and south slopes of Mount Hood, flow approximately 55 miles in a northwesterly direction and enter the Columbia River near Troutdale ...

  Citation × Citation Citation Abstract Copy Title: Sandy River Basin Fish Management Plan 1997 Draft Abstract -- The Sandy River and its tributaries originate high on the west and south slopes of Mount Hood, flow approximately 55 miles in a northwesterly direction and enter the Columbia River near Troutdale (Columbia RM 120.5). The Sandy basin is situated in Multnomah and Clackamas counties (EPA reach 17080001), and drains approximately 508 square miles. The Sandy River basin is comprised of several subbasins, many of which are uniquely distinct hydrologically and geomorphologically. Principle tributaries include the Zigzag River, Still Creek, and the Salmon River in the upper basin and the Bull Run River, Gordon, Cedar, and Beaver creeks in the lower basin. Many other smaller tributaries located throughout the basin contribute significantly to stream flows and provide habitat for a wide array of fish and wildlife assemblages. The Sandy River is well known for its sport fishing. Winter steelhead, summer steelhead, and spring chinook are the most sought after species. Both winter and summer steelhead, coho, and spring chinook are supplemented with hatchery produced fish. Rainbow trout and fall chinook are no longer stocked in flowing waters of the Sandy River basin. In the late 1980's the Northwest Power Planning Council administered a planning process to create a management plan for the Columbia River basin. As a part of that process, a subbasin plan concerning management of steelhead and salmon was written for the Sandy River basin. This document, the draft "Sandy River Basin Fish Management Plan", significantly expands on the Northwest Power Planning Council document by adding resident fish species and new information on anadromous species and will ultimately produce the final plan used to guide fish resource management in the basin for the next 5 to 10 years. Title: Sandy River Basin Fish Management Plan 1997 Draft Abstract -- The Sandy River and its tributaries originate high on the west and south slopes of Mount Hood, flow approximately 55 miles in a northwesterly direction and enter the Columbia River near Troutdale (Columbia RM 120.5). The Sandy basin is situated in Multnomah and Clackamas counties (EPA reach 17080001), and drains approximately 508 square miles. The Sandy River basin is comprised of several subbasins, many of which are uniquely distinct hydrologically and geomorphologically. Principle tributaries include the Zigzag River, Still Creek, and the Salmon River in the upper basin and the Bull Run River, Gordon, Cedar, and Beaver creeks in the lower basin. Many other smaller tributaries located throughout the basin contribute significantly to stream flows and provide habitat for a wide array of fish and wildlife assemblages. The Sandy River is well known for its sport fishing. Winter steelhead, summer steelhead, and spring chinook are the most sought after species. Both winter and summer steelhead, coho, and spring chinook are supplemented with hatchery produced fish. Rainbow trout and fall chinook are no longer stocked in flowing waters of the Sandy River basin. In the late 1980's the Northwest Power Planning Council administered a planning process to create a management plan for the Columbia River basin. As a part of that process, a subbasin plan concerning management of steelhead and salmon was written for the Sandy River basin. This document, the draft "Sandy River Basin Fish Management Plan", significantly expands on the Northwest Power Planning Council document by adding resident fish species and new information on anadromous species and will ultimately produce the final plan used to guide fish resource management in the basin for the next 5 to 10 years. Close

• 1832. [Article] Fifteenmile Creek Subbasin Fish Management Plan 1992

  Abstract -- This plan encompasses the flowing waters of the Fifteenmile Creek drainage. It was adapted from the Northwest Power Planning council's (NPPC) Fifteenmile Creek Subbasin Plan, which in turn ...

  Citation × Citation Citation Abstract Copy Title: Fifteenmile Creek Subbasin Fish Management Plan 1992 Abstract -- This plan encompasses the flowing waters of the Fifteenmile Creek drainage. It was adapted from the Northwest Power Planning council's (NPPC) Fifteenmile Creek Subbasin Plan, which in turn was developed by the Oregon Department of Fish and Wildlife (ODFW) and the confederated Tribes of the Warm Springs Reservation of Oregon (CTWSR) with the help of three committees. The Public Advisory Committee, representing non-treaty user groups and other interested public, helped identify a range of objectives and actions for managing the fishery resources in the Fifteenmile Creek drainage. The Technical Committee, composed of representatives of state and federal fishery agencies, tribes, land and water management agencies, and utilities, developed specific fishery and other technical information and described and assessed potential actions for managing the fisheries. The Fish Management Committee, composed of representatives of Oregon Department of Fish and Wildlife and the Warm Springs Tribe, selected a preferred range of objectives and actions. The Northwest Power Planning Council's Fifteenmile Creek Subbasin Plan was one of 31 subbasin plans incorporated into the NPPC's Integrated system Plan in an attempt to double the run sizes of anadromous salmonids in the Columbia River Basin. Title: Fifteenmile Creek Subbasin Fish Management Plan 1992 Abstract -- This plan encompasses the flowing waters of the Fifteenmile Creek drainage. It was adapted from the Northwest Power Planning council's (NPPC) Fifteenmile Creek Subbasin Plan, which in turn was developed by the Oregon Department of Fish and Wildlife (ODFW) and the confederated Tribes of the Warm Springs Reservation of Oregon (CTWSR) with the help of three committees. The Public Advisory Committee, representing non-treaty user groups and other interested public, helped identify a range of objectives and actions for managing the fishery resources in the Fifteenmile Creek drainage. The Technical Committee, composed of representatives of state and federal fishery agencies, tribes, land and water management agencies, and utilities, developed specific fishery and other technical information and described and assessed potential actions for managing the fisheries. The Fish Management Committee, composed of representatives of Oregon Department of Fish and Wildlife and the Warm Springs Tribe, selected a preferred range of objectives and actions. The Northwest Power Planning Council's Fifteenmile Creek Subbasin Plan was one of 31 subbasin plans incorporated into the NPPC's Integrated system Plan in an attempt to double the run sizes of anadromous salmonids in the Columbia River Basin. Close

• 1833. [Article] Oregon Chub Investigations, Progress Report 2001

  Abstract -- Populations of Oregon chub Oregonichthys crameri, endemic to the Willamette Valley, have been drastically reduced. Factors in the decline of this fish include changes in flow regimes and habitat ...

  Citation × Citation Citation Abstract Copy Title: Oregon Chub Investigations, Progress Report 2001 Abstract -- Populations of Oregon chub Oregonichthys crameri, endemic to the Willamette Valley, have been drastically reduced. Factors in the decline of this fish include changes in flow regimes and habitat characteristics resulting from the construction of flood control dams, revetments, channelization, diking, and the drainage of wetlands. The Oregon chub is further threatened by predation and competition by non-native species such as largemouth bass Micropterus salmoides, small mouth bass M. dolomieui, crappies Pomoxis sp., sunfishes Lepomis sp., bullheads Ameiurus sp., and western mosquitofish Gambusia affinis. We surveyed in the Willamette River drainage in April-October 2000 to quantify existing Oregon chub populations, search for unknown populations, evaluate potential introduction sites, and monitor introduced populations. We sampled a total of 77 sites in 2000. We collected Oregon chub for the first time from Barnard Slough in the Middle Fork Willamette drainage. Oregon chub were last collected from this location in 1983 (Bond 1984). Thirty-one of the 77 sites were new sites that were sampled for the first time in 2000. Forty-six sites, sampled in 1991-1999, were revisited. Three sites were sampled twice. We confirmed the continued existence of Oregon chub at 20 locations. These include naturally occurring populations in the Santiam drainage (Geren Island, Santiam Conservation Easement, Gray Slough, Santiam 1-5 backwaters, Pioneer Park backwater, Santiam Public Works Pond), Mid-Willamette drainage (Finley Gray Creek Swamp) and Middle Fork Willamette drainage (Dexter Reservoir Alcoves, East Fork Minnow Creek Pond, Shady Dell Pond, Buckhead Creek, Oakridge Slough, Elijah Bristow State Park, Rattlesnake Creek, and Hospital Pond) and introduced populations in the Middle Fork Willamette (Wicopee Pond, Fall Creek Spillway Ponds), Santiam (Foster Pullout Pond), and Mid-Willamette drainages (Dunn Wetland, Finley Display Pond). Oregon chub were not found at several locations (Jasper Park Slough, Wallace Slough, East Ferrin Pond, Dexter East Alcove, Hospital lmpoundment Pond, Logan Slough, Green's Bridge Backwater, Camas Swale) where they were collected on at least one occasion between 1991-1999 (Scheerer et. al. 1992; 1993; 1994; 1995; 1996; 1998; 1999; 2000; Scheerer and Jones 1997). Non-native fish were common in off-channel habitats that were surveyed in the Willamette River drainage. Non-native fish were collected from 23 of the 31 new sites sampled in 1999 (74%); no fish were collected at three locations (10%). Western mosquitofish and centrarchids (largemouth bass and bluegill) were the most common non-native fish collected. Oregon chub were introduced into Menear's Bend Pond in the Santiam River drainage in the October 2000. Additional Oregon chub were introduced into Foster Pullout Pond in October 2000, to supplement the 85 fish introduced in 1999. In the summer of 2000, a habitat enhancement project creating new habitat to benefit Oregon chub was completed in the Long Tom drainage (Mid-Willamette River). Seven potential Oregon chub reintroduction sites were monitored and evaluated. These included four sites in the Mid-Willamette River drainage (Finley National Wildlife Refuge Beaver and Cattail Ponds, Ankeny National Wildlife Refuge Dunlin-Woodduck Pond, Long Tom Ranch Pond), one site in the Santiam River drainage (Menear's Bend Pond), one site in the McKenzie River drainage (Russell Pond), and one site in the Coast Fork Willamette drainage (Layng Pond). Estimates of abundance were obtained for naturally occurring populations of Oregon chub in East Fork Minnow Creek Pond, Shady Dell Pond, Elijah Bristow State Park Sloughs, Hospital Pond, Dexter Reservoir Alcoves, Buckhead Creek, Oakridge Slough, Santiam Conservation Easement Sloughs, Geren Island Ponds, and Finley Gray Creek Swamp. Five of these populations showed an increase in abundance in 2000 (East Fork Minnow Creek Pond, Shady Dell Pond, Middle Buckhead Creek, Dexter Reservoir Alcoves, Finley Gray Creek Swamp). Four populations decreased in abundance (or remain depressed) in 2000 (Geren Island, Santiam Conservation Easement, Elijah Bristow Sloughs, Oakridge Slough) (Table 1 ). Abundance estimates for introduced populations of Oregon chub were also obtained. The Oregon chub population in East Ferrin Pond declined from 7,200 fish in 1997 to O fish in 2000, and is presumed extinct. The Oregon chub population in the Fall Creek Spillway Pond totaled 5,030 fish in 2000, compared to 6,300 fish in 1999. The Oregon chub population in Wicopee Pond expanded dramatically from ~50 fish in 1999 to 4,580 fish in 2000. The Oregon chub population in the Dunn Wetland Ponds increased from 4,860 fish in 1999 to 14,090 fish in 2000. The Oregon chub population in Finley Display Pond increased from 360 fish in 1999 to 1,750 fish in 2000. Three of the four largest populations in 2000 were introduced populations. The Middle Fork Willamette River drainage supported the largest number of Oregon chub populations (n=12), followed by the Santiam drainage (n=B), and the Mid-Willamette drainage (n=5). The most abundant Oregon chub populations were found in the Middle Fork Willamette and Mid-Willamette drainages. The Oregon Chub Recovery Plan (U .S. Fish and Wildlife Service 1998) set a recovery goal for downlisting the species to "threatened" and for delisting the species. The criteria for downlisting the species was to establish and manage ten populations of at least 500 adult fish. All populations must exhibit a stable or increasing trend for five years. At least three populations must be located in each of the three sub-basins (Middle Fork Willamette River, Santiam River, Mid-Willamette River tributaries). In 2000, there were 11 populations totaling 500 or more individuals and six of these populations exhibited a stable or increasing trend for the past five years (Table 1 ). Five of these six populations were located in the Middle Fork Willamette drainage. In summary, Oregon chub remain at risk due to their limited distribution compared with their historic geographic range in the Willamette Valley, the loss of suitable habitat and the continued threats posed by the proliferation of non-native fishes, illegal water withdrawals, unauthorized fill and removal operations, and potential chemical spills or careless pesticide applications. Title: Oregon Chub Investigations, Progress Report 2001 Abstract -- Populations of Oregon chub Oregonichthys crameri, endemic to the Willamette Valley, have been drastically reduced. Factors in the decline of this fish include changes in flow regimes and habitat characteristics resulting from the construction of flood control dams, revetments, channelization, diking, and the drainage of wetlands. The Oregon chub is further threatened by predation and competition by non-native species such as largemouth bass Micropterus salmoides, small mouth bass M. dolomieui, crappies Pomoxis sp., sunfishes Lepomis sp., bullheads Ameiurus sp., and western mosquitofish Gambusia affinis. We surveyed in the Willamette River drainage in April-October 2000 to quantify existing Oregon chub populations, search for unknown populations, evaluate potential introduction sites, and monitor introduced populations. We sampled a total of 77 sites in 2000. We collected Oregon chub for the first time from Barnard Slough in the Middle Fork Willamette drainage. Oregon chub were last collected from this location in 1983 (Bond 1984). Thirty-one of the 77 sites were new sites that were sampled for the first time in 2000. Forty-six sites, sampled in 1991-1999, were revisited. Three sites were sampled twice. We confirmed the continued existence of Oregon chub at 20 locations. These include naturally occurring populations in the Santiam drainage (Geren Island, Santiam Conservation Easement, Gray Slough, Santiam 1-5 backwaters, Pioneer Park backwater, Santiam Public Works Pond), Mid-Willamette drainage (Finley Gray Creek Swamp) and Middle Fork Willamette drainage (Dexter Reservoir Alcoves, East Fork Minnow Creek Pond, Shady Dell Pond, Buckhead Creek, Oakridge Slough, Elijah Bristow State Park, Rattlesnake Creek, and Hospital Pond) and introduced populations in the Middle Fork Willamette (Wicopee Pond, Fall Creek Spillway Ponds), Santiam (Foster Pullout Pond), and Mid-Willamette drainages (Dunn Wetland, Finley Display Pond). Oregon chub were not found at several locations (Jasper Park Slough, Wallace Slough, East Ferrin Pond, Dexter East Alcove, Hospital lmpoundment Pond, Logan Slough, Green's Bridge Backwater, Camas Swale) where they were collected on at least one occasion between 1991-1999 (Scheerer et. al. 1992; 1993; 1994; 1995; 1996; 1998; 1999; 2000; Scheerer and Jones 1997). Non-native fish were common in off-channel habitats that were surveyed in the Willamette River drainage. Non-native fish were collected from 23 of the 31 new sites sampled in 1999 (74%); no fish were collected at three locations (10%). Western mosquitofish and centrarchids (largemouth bass and bluegill) were the most common non-native fish collected. Oregon chub were introduced into Menear's Bend Pond in the Santiam River drainage in the October 2000. Additional Oregon chub were introduced into Foster Pullout Pond in October 2000, to supplement the 85 fish introduced in 1999. In the summer of 2000, a habitat enhancement project creating new habitat to benefit Oregon chub was completed in the Long Tom drainage (Mid-Willamette River). Seven potential Oregon chub reintroduction sites were monitored and evaluated. These included four sites in the Mid-Willamette River drainage (Finley National Wildlife Refuge Beaver and Cattail Ponds, Ankeny National Wildlife Refuge Dunlin-Woodduck Pond, Long Tom Ranch Pond), one site in the Santiam River drainage (Menear's Bend Pond), one site in the McKenzie River drainage (Russell Pond), and one site in the Coast Fork Willamette drainage (Layng Pond). Estimates of abundance were obtained for naturally occurring populations of Oregon chub in East Fork Minnow Creek Pond, Shady Dell Pond, Elijah Bristow State Park Sloughs, Hospital Pond, Dexter Reservoir Alcoves, Buckhead Creek, Oakridge Slough, Santiam Conservation Easement Sloughs, Geren Island Ponds, and Finley Gray Creek Swamp. Five of these populations showed an increase in abundance in 2000 (East Fork Minnow Creek Pond, Shady Dell Pond, Middle Buckhead Creek, Dexter Reservoir Alcoves, Finley Gray Creek Swamp). Four populations decreased in abundance (or remain depressed) in 2000 (Geren Island, Santiam Conservation Easement, Elijah Bristow Sloughs, Oakridge Slough) (Table 1 ). Abundance estimates for introduced populations of Oregon chub were also obtained. The Oregon chub population in East Ferrin Pond declined from 7,200 fish in 1997 to O fish in 2000, and is presumed extinct. The Oregon chub population in the Fall Creek Spillway Pond totaled 5,030 fish in 2000, compared to 6,300 fish in 1999. The Oregon chub population in Wicopee Pond expanded dramatically from ~50 fish in 1999 to 4,580 fish in 2000. The Oregon chub population in the Dunn Wetland Ponds increased from 4,860 fish in 1999 to 14,090 fish in 2000. The Oregon chub population in Finley Display Pond increased from 360 fish in 1999 to 1,750 fish in 2000. Three of the four largest populations in 2000 were introduced populations. The Middle Fork Willamette River drainage supported the largest number of Oregon chub populations (n=12), followed by the Santiam drainage (n=B), and the Mid-Willamette drainage (n=5). The most abundant Oregon chub populations were found in the Middle Fork Willamette and Mid-Willamette drainages. The Oregon Chub Recovery Plan (U .S. Fish and Wildlife Service 1998) set a recovery goal for downlisting the species to "threatened" and for delisting the species. The criteria for downlisting the species was to establish and manage ten populations of at least 500 adult fish. All populations must exhibit a stable or increasing trend for five years. At least three populations must be located in each of the three sub-basins (Middle Fork Willamette River, Santiam River, Mid-Willamette River tributaries). In 2000, there were 11 populations totaling 500 or more individuals and six of these populations exhibited a stable or increasing trend for the past five years (Table 1 ). Five of these six populations were located in the Middle Fork Willamette drainage. In summary, Oregon chub remain at risk due to their limited distribution compared with their historic geographic range in the Willamette Valley, the loss of suitable habitat and the continued threats posed by the proliferation of non-native fishes, illegal water withdrawals, unauthorized fill and removal operations, and potential chemical spills or careless pesticide applications. Close

• 1834. [Article] Progress Reports 2004: 2004 Oregon Chub Investigations

  Abstract -- Oregon chub are endemic to the Willamette River drainage of western Oregon (Markle et al. 1991). This species was formerly distributed throughout the Willamette River Valley (Snyder 1908) in ...

  Citation × Citation Citation Abstract Copy Title: Progress Reports 2004: 2004 Oregon Chub Investigations Abstract -- Oregon chub are endemic to the Willamette River drainage of western Oregon (Markle et al. 1991). This species was formerly distributed throughout the Willamette River Valley (Snyder 1908) in off-channel habitats such as beaver ponds, oxbows, stable backwater sloughs, and flooded marshes. These habitats usually have little or no water flow, have silty and organic substrate, and have an abundance of aquatic vegetation and cover for hiding and spawning. In the last 100 years, off-channel habitats have disappeared because of changes in seasonal flows resulting from the construction of dams throughout the basin, channelization of the Willamette River and its tributaries, and agricultural practices. This loss of habitat combined with the introduction of non-native species to the Willamette Valley resulted in a sharp decline in Oregon chub abundance. The reduction of habitat and the restricted distribution of the Oregon chub resulted in a determination of "endangered" status under the federal endangered species act (Markle and Pearsons 1990; Rhew 1993). To evaluate Oregon chub population abundance and distribution, the Oregon Department of Fish and Wildlife conducted surveys in April-October 2004. We conducted similar surveys in 1991-2003 (Scheerer et. al. 1992; 1993; 1994; 1995; 1996; 1998; 1999; 2000; 2001; 2002; 2003; 2004; Scheerer and Jones 1997). The survey objectives were to collect information on the status, distribution, and abundance of Oregon chub, the presence of non-native and native species, the characteristics of Oregon chub habitats, the characteristics of potential introduction sites, and to evaluate the success of Oregon chub introductions. In addition, we reviewed and evaluated projects and activities with the potential to impact Oregon chub and their habitats and provided summaries to the U.S. Fish and Wildlife Service. Title: Progress Reports 2004: 2004 Oregon Chub Investigations Abstract -- Oregon chub are endemic to the Willamette River drainage of western Oregon (Markle et al. 1991). This species was formerly distributed throughout the Willamette River Valley (Snyder 1908) in off-channel habitats such as beaver ponds, oxbows, stable backwater sloughs, and flooded marshes. These habitats usually have little or no water flow, have silty and organic substrate, and have an abundance of aquatic vegetation and cover for hiding and spawning. In the last 100 years, off-channel habitats have disappeared because of changes in seasonal flows resulting from the construction of dams throughout the basin, channelization of the Willamette River and its tributaries, and agricultural practices. This loss of habitat combined with the introduction of non-native species to the Willamette Valley resulted in a sharp decline in Oregon chub abundance. The reduction of habitat and the restricted distribution of the Oregon chub resulted in a determination of "endangered" status under the federal endangered species act (Markle and Pearsons 1990; Rhew 1993). To evaluate Oregon chub population abundance and distribution, the Oregon Department of Fish and Wildlife conducted surveys in April-October 2004. We conducted similar surveys in 1991-2003 (Scheerer et. al. 1992; 1993; 1994; 1995; 1996; 1998; 1999; 2000; 2001; 2002; 2003; 2004; Scheerer and Jones 1997). The survey objectives were to collect information on the status, distribution, and abundance of Oregon chub, the presence of non-native and native species, the characteristics of Oregon chub habitats, the characteristics of potential introduction sites, and to evaluate the success of Oregon chub introductions. In addition, we reviewed and evaluated projects and activities with the potential to impact Oregon chub and their habitats and provided summaries to the U.S. Fish and Wildlife Service. Close

• 1835. [Article] Columbia River (Bonneville Dam to Washington Border) Master Plan for Angler Access and Associated Recreational Uses 1969

  Abstract -- This plan covers the 163 miles of the Columbia between Bonneville Dam and the Washington state line. This part of the river has been dammed at four places to form four large impoundments eliminating ...

  Citation × Citation Citation Abstract Copy Title: Columbia River (Bonneville Dam to Washington Border) Master Plan for Angler Access and Associated Recreational Uses 1969 Abstract -- This plan covers the 163 miles of the Columbia between Bonneville Dam and the Washington state line. This part of the river has been dammed at four places to form four large impoundments eliminating the rugged, free flowing character that the mighty Columbia once had . The only free flowing river that remains lies directly below each of the dams. The fishing potential in the impoundments is minimal. These large expanses of slack water have made ideal rearing areas for squawfish, suckers and other rough fish which severely limit populations of bass, crappie, catfish and other warm-water game fish that could provide a good fishery. The exception is at Cascade Locks where salmon, steelhead, shad and sturgeon are taken within the Bonneville Pool. Sturgeon also provide some sport in other areas of the Bonneville Pool. The only significant fishery that remains is in the free flowing sections below the dams where steelhead and salmon are caught. The spill area below McNary Dam is a good example; however, a fishery has not yet developed below The Dalles and John Day Dams. Title: Columbia River (Bonneville Dam to Washington Border) Master Plan for Angler Access and Associated Recreational Uses 1969 Abstract -- This plan covers the 163 miles of the Columbia between Bonneville Dam and the Washington state line. This part of the river has been dammed at four places to form four large impoundments eliminating the rugged, free flowing character that the mighty Columbia once had . The only free flowing river that remains lies directly below each of the dams. The fishing potential in the impoundments is minimal. These large expanses of slack water have made ideal rearing areas for squawfish, suckers and other rough fish which severely limit populations of bass, crappie, catfish and other warm-water game fish that could provide a good fishery. The exception is at Cascade Locks where salmon, steelhead, shad and sturgeon are taken within the Bonneville Pool. Sturgeon also provide some sport in other areas of the Bonneville Pool. The only significant fishery that remains is in the free flowing sections below the dams where steelhead and salmon are caught. The spill area below McNary Dam is a good example; however, a fishery has not yet developed below The Dalles and John Day Dams. Close

• 1836. [Article] Deschutes, Little Deschutes and Metolius Master Plan for Angler Access and Associated Recreational Uses 1969

  Abstract -- This basin is located in the north central part of the state and drains an area covering nearly 11 percent of the state . The Cascade Mountains range on the west, lava plateaus lie to the south, ...

  Citation × Citation Citation Abstract Copy Title: Deschutes, Little Deschutes and Metolius Master Plan for Angler Access and Associated Recreational Uses 1969 Abstract -- This basin is located in the north central part of the state and drains an area covering nearly 11 percent of the state . The Cascade Mountains range on the west, lava plateaus lie to the south, and the Ochoco Mountains and a large plateau border on the east. The Deschutes River proper flows some 250 miles in its journey from the south to join the Columbia River near The Dalles . Its tributary system is vast and includes several minor rivers of which all but Crooked River will be covered in this report. The basin offers some of the finest outdoor recreation opportunities in the West. Fed by melting snow and by springs emerging from lava flows in the east side of the Cascades, the river maintains a remarkably even flow of clear, cold water the year round. It is one of the top steelhead and trout streams of the country; the canyon and adjoining lands offer superb scenery and abundant game including mule deer, chukars, quail, and other upland game birds. The weather is ideal for many forms of outdoor recreation all seasons of the year. This report details a plan that we hope can be followed to solve the access problems of the Deschutes, Little Deschutes and Metolius Rivers . Title: Deschutes, Little Deschutes and Metolius Master Plan for Angler Access and Associated Recreational Uses 1969 Abstract -- This basin is located in the north central part of the state and drains an area covering nearly 11 percent of the state . The Cascade Mountains range on the west, lava plateaus lie to the south, and the Ochoco Mountains and a large plateau border on the east. The Deschutes River proper flows some 250 miles in its journey from the south to join the Columbia River near The Dalles . Its tributary system is vast and includes several minor rivers of which all but Crooked River will be covered in this report. The basin offers some of the finest outdoor recreation opportunities in the West. Fed by melting snow and by springs emerging from lava flows in the east side of the Cascades, the river maintains a remarkably even flow of clear, cold water the year round. It is one of the top steelhead and trout streams of the country; the canyon and adjoining lands offer superb scenery and abundant game including mule deer, chukars, quail, and other upland game birds. The weather is ideal for many forms of outdoor recreation all seasons of the year. This report details a plan that we hope can be followed to solve the access problems of the Deschutes, Little Deschutes and Metolius Rivers . Close

• 1837. [Article] John Day River Basin Master Plan for Angler Access and Associated Recreational Uses 1967

  Abstract -- The John Day Basin is located in the north central part of the state and covers an area of approximately 8,010 square miles. This includes nearly all of Wheeler, Gilliam and Grant Counties, ...

  Citation × Citation Citation Abstract Copy Title: John Day River Basin Master Plan for Angler Access and Associated Recreational Uses 1967 Abstract -- The John Day Basin is located in the north central part of the state and covers an area of approximately 8,010 square miles. This includes nearly all of Wheeler, Gilliam and Grant Counties, and portions of Sherman, Umatilla, Morrow, Jefferson, Wasco, Crook, Harney and Union Counties. The John Day heads in the Blue Mountains southeast of Prairie City and flows into the Columbia near Biggs. There are 4,350 streams in the system which total approximately 9,500 miles in length. Agriculture is the major source of income to the basin. The fishery is quite diversified within the basin. Steelhead, trout, whitefish and warm-water species are available for anglers. In addition to these fish, spring Chinook and coho salmon are also within the system. The John Day Basin has been divided into five sections and each has been handled according to its individual needs. The report sections describe these areas more fully and each site is described in detail. Title: John Day River Basin Master Plan for Angler Access and Associated Recreational Uses 1967 Abstract -- The John Day Basin is located in the north central part of the state and covers an area of approximately 8,010 square miles. This includes nearly all of Wheeler, Gilliam and Grant Counties, and portions of Sherman, Umatilla, Morrow, Jefferson, Wasco, Crook, Harney and Union Counties. The John Day heads in the Blue Mountains southeast of Prairie City and flows into the Columbia near Biggs. There are 4,350 streams in the system which total approximately 9,500 miles in length. Agriculture is the major source of income to the basin. The fishery is quite diversified within the basin. Steelhead, trout, whitefish and warm-water species are available for anglers. In addition to these fish, spring Chinook and coho salmon are also within the system. The John Day Basin has been divided into five sections and each has been handled according to its individual needs. The report sections describe these areas more fully and each site is described in detail. Close

• 1838. [Article] Survey of the Waters of South Umpqua Ranger District, Umpqua National Forest, 1937

  Abstract -- The objectives of the present survey of the upper waters of the South Fork of the Umpqua River were to: (1) develop practical and scientifically sound stocking policies; (2) determine the need ...

  Citation × Citation Citation Abstract Copy Title: Survey of the Waters of South Umpqua Ranger District, Umpqua National Forest, 1937 Abstract -- The objectives of the present survey of the upper waters of the South Fork of the Umpqua River were to: (1) develop practical and scientifically sound stocking policies; (2) determine the need for stream and lake improvements; and (3) obtain facts to assist in the settlement of the controversy with regard to the South Umpqua Falls. There has been continual demand by sportsmen that the South Umpqua Falls be supplied with fish ladders to permit safe ascent of sea-run species to spawning grounds above the falls. Study of this problem was undertaken as a definite part of the survey work described herein. The stream run and lake survey work was initiated by the Forest Service in cooperation with the U.S. Bureau of Fisheries during the summer of 1937. Emphasis was placed on the detailed studies relating to the physical and biological factors upon which it would be possible to recommend adequate stocking policies. No study of chemical conditions whatsoever was made for two reasons, first, lack of equipment prevented making gas analyses and, second, such studies seemed unnecessary by reason of the fact that there is no pollution present in the streams surveyed and all of them are well aerated, clean, rapid flowing mountain streams. Chemical conditions as shown by general observations were quite suitable and it is only whore natural or artificial pollutants occur in great abundance that chemical analyses would aid in determining tho basic effects of some of those fishes and their food organisms present in streams. Title: Survey of the Waters of South Umpqua Ranger District, Umpqua National Forest, 1937 Abstract -- The objectives of the present survey of the upper waters of the South Fork of the Umpqua River were to: (1) develop practical and scientifically sound stocking policies; (2) determine the need for stream and lake improvements; and (3) obtain facts to assist in the settlement of the controversy with regard to the South Umpqua Falls. There has been continual demand by sportsmen that the South Umpqua Falls be supplied with fish ladders to permit safe ascent of sea-run species to spawning grounds above the falls. Study of this problem was undertaken as a definite part of the survey work described herein. The stream run and lake survey work was initiated by the Forest Service in cooperation with the U.S. Bureau of Fisheries during the summer of 1937. Emphasis was placed on the detailed studies relating to the physical and biological factors upon which it would be possible to recommend adequate stocking policies. No study of chemical conditions whatsoever was made for two reasons, first, lack of equipment prevented making gas analyses and, second, such studies seemed unnecessary by reason of the fact that there is no pollution present in the streams surveyed and all of them are well aerated, clean, rapid flowing mountain streams. Chemical conditions as shown by general observations were quite suitable and it is only whore natural or artificial pollutants occur in great abundance that chemical analyses would aid in determining tho basic effects of some of those fishes and their food organisms present in streams. Close