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• 1. [Image] Genetics, demography, monitoring and restoration of Mt. Mazama Collomia

  	ill. (some color); maps; Funded by: Canon USA's "Expedition into the Parks." This work includes Phase I and Phase II.; "Mt. Mazama Collomia (Collomia mazama) is a beautiful and rare member of the Phlox ...
  	Citation × Citation Citation Abstract Copy Title: Genetics, demography, monitoring and restoration of Mt. Mazama Collomia Author: Baldwin, Caleb T. Year: 2001, 2008, 2009 ill. (some color); maps; Funded by: Canon USA's "Expedition into the Parks." This work includes Phase I and Phase II.; "Mt. Mazama Collomia (Collomia mazama) is a beautiful and rare member of the Phlox family endemic to Crater Lake National Park and adjacent lands on the Rogue River ... . It is a perennial species primarily restricted to the open woods and meadows of the lodgepole pine and true fir forest zones of the southern Cascade Mountains. ...originally discovered along Dutton Creek near Crater Lake in 1896, by ... F.V. Coville... ." - Intro.; Includes bibliographical references on multiple pages throughout the work; Title: Genetics, demography, monitoring and restoration of Mt. Mazama Collomia Author: Baldwin, Caleb T. Year: 2001, 2008, 2009 ill. (some color); maps; Funded by: Canon USA's "Expedition into the Parks." This work includes Phase I and Phase II.; "Mt. Mazama Collomia (Collomia mazama) is a beautiful and rare member of the Phlox family endemic to Crater Lake National Park and adjacent lands on the Rogue River ... . It is a perennial species primarily restricted to the open woods and meadows of the lodgepole pine and true fir forest zones of the southern Cascade Mountains. ...originally discovered along Dutton Creek near Crater Lake in 1896, by ... F.V. Coville... ." - Intro.; Includes bibliographical references on multiple pages throughout the work; Close

• 2. [Image] Hot Dry Rock Geothermal Energy Development Program. Annual Report, Fiscal Year 1983

  	Emphasis was on hydraulic-fracturing experiments at depths around 3.5 km (11,473 ft) in the two inclined wells of the Phase II system at Fenton Hill, New Mexico; on improved facilities and techniques for ...
  	Citation × Citation Citation Abstract Copy Title: Hot Dry Rock Geothermal Energy Development Program. Annual Report, Fiscal Year 1983 Author: Smith, M.C. (comp.) Year: 1985 Emphasis was on hydraulic-fracturing experiments at depths around 3.5 km (11,473 ft) in the two inclined wells of the Phase II system at Fenton Hill, New Mexico; on improved facilities and techniques for mapping the source locations of acoustic signals generated by the fracturing events; on mathematical modeling of the fracture systems produced in these and earlier experiments; and on development of a family of slimline high-temperature downhole instruments that can be used within or through relatively small-diameter pressure tubing. Hydraulic fracturing at a vertical depth of approximately 3500 m (11,500 ft) in well EE-2, the deeper well, produced fractures that, in acoustic maps, appear to occupy a large, roughly ellipsoidal volume whose major axis is directed to the north of the other well, EE-3. Hydraulic fracturing from EE-3 at a similar depth produced another set of fractures that appear to be approximately parallel to and centered about 180 m (600 ft) east of the earlier set. Subsequent fluid injections reduced the distance between the two sets, but no hydraulic connection between them was established. Modeling the silica concentrations of fluid circulated through the earlier Phase I system indicates that this type of permeation also contributes significantly to heat extraction during system operation. The precision and accuracy of locating the sources of acoustic signals detected during hydraulic-fracturing operations have been increased by improvements in equipment, drilling of another deep hole for geophone emplacement, and additional station calibrations. Analysis of the signals has also been improved and broadened. Development of slimline downhole instruments has included a detonator tool, a geophone package, and final design of a high-temperature borehole acoustic televiewer. A crosswell acoustic transceiver has also been developed for investigating rock type and structure between wellbores. 32 refs., 35 figs. Title: Hot Dry Rock Geothermal Energy Development Program. Annual Report, Fiscal Year 1983 Author: Smith, M.C. (comp.) Year: 1985 Emphasis was on hydraulic-fracturing experiments at depths around 3.5 km (11,473 ft) in the two inclined wells of the Phase II system at Fenton Hill, New Mexico; on improved facilities and techniques for mapping the source locations of acoustic signals generated by the fracturing events; on mathematical modeling of the fracture systems produced in these and earlier experiments; and on development of a family of slimline high-temperature downhole instruments that can be used within or through relatively small-diameter pressure tubing. Hydraulic fracturing at a vertical depth of approximately 3500 m (11,500 ft) in well EE-2, the deeper well, produced fractures that, in acoustic maps, appear to occupy a large, roughly ellipsoidal volume whose major axis is directed to the north of the other well, EE-3. Hydraulic fracturing from EE-3 at a similar depth produced another set of fractures that appear to be approximately parallel to and centered about 180 m (600 ft) east of the earlier set. Subsequent fluid injections reduced the distance between the two sets, but no hydraulic connection between them was established. Modeling the silica concentrations of fluid circulated through the earlier Phase I system indicates that this type of permeation also contributes significantly to heat extraction during system operation. The precision and accuracy of locating the sources of acoustic signals detected during hydraulic-fracturing operations have been increased by improvements in equipment, drilling of another deep hole for geophone emplacement, and additional station calibrations. Analysis of the signals has also been improved and broadened. Development of slimline downhole instruments has included a detonator tool, a geophone package, and final design of a high-temperature borehole acoustic televiewer. A crosswell acoustic transceiver has also been developed for investigating rock type and structure between wellbores. 32 refs., 35 figs. Close

• 3. [Image] Crater Lake National Park visitor study, summer 2001

  	chiefly ill., maps; "The visitor study was conducted August 3-9, 2001 by the National Park Service (NPS) Visitor Services Project (VSP), part of the Cooperative Park Studies Unit at the University of ...
  	Citation × Citation Citation Abstract Copy Title: Crater Lake National Park visitor study, summer 2001 Author: Littlejohn, Margaret Year: 2002, 2009 chiefly ill., maps; "The visitor study was conducted August 3-9, 2001 by the National Park Service (NPS) Visitor Services Project (VSP), part of the Cooperative Park Studies Unit at the University of Idaho"--P. 1.; "April 2002."; "NPS D-313"--Last printed p. Title: Crater Lake National Park visitor study, summer 2001 Author: Littlejohn, Margaret Year: 2002, 2009 chiefly ill., maps; "The visitor study was conducted August 3-9, 2001 by the National Park Service (NPS) Visitor Services Project (VSP), part of the Cooperative Park Studies Unit at the University of Idaho"--P. 1.; "April 2002."; "NPS D-313"--Last printed p. Close

• 4. [Image] Applications of Thermal Energy Storage To Process Heat and Waste Heat Recovery in the Primary Aluminum Industry - Final Report for the Period September 1977 - September 1978

  	In this preliminary study, a system has been identified by which the large amounts of lowgrade waste energy in the primary pollution control system gas :stream can be utilized for comfort heating in nearby ...
  	Citation × Citation Citation Abstract Copy Title: Applications of Thermal Energy Storage To Process Heat and Waste Heat Recovery in the Primary Aluminum Industry - Final Report for the Period September 1977 - September 1978 Author: Hoskins, R.L. Year: 1978 In this preliminary study, a system has been identified by which the large amounts of lowgrade waste energy in the primary pollution control system gas :stream can be utilized for comfort heating in nearby communities. Energy is stored in the form of hot water, contained in conventional, insulated steel tanks, enabling a morel' efficient utilization of the constant energy source by the cyclical energy demand. Less expensive energy storage means (heated ponds, aquifers), when they become fully characterized, will allow even more cost-competitive systems. Extensive design tradeoff studies have been performed for the example site, Intalco Aluminum Corporation and the surrounding communities of Ferndale and Bellingham, Washington. These tradeoff studies indicate that a heating demand equivalent to 12,000 single-family residences can be supplied by the energy from the Intalco site. Using a .30-year payback criterion (consistent with utility planning practice), the average cost of energy supplied over the system useful life is predicted at one-third the average cost of fossil fuel Title: Applications of Thermal Energy Storage To Process Heat and Waste Heat Recovery in the Primary Aluminum Industry - Final Report for the Period September 1977 - September 1978 Author: Hoskins, R.L. Year: 1978 In this preliminary study, a system has been identified by which the large amounts of lowgrade waste energy in the primary pollution control system gas :stream can be utilized for comfort heating in nearby communities. Energy is stored in the form of hot water, contained in conventional, insulated steel tanks, enabling a morel' efficient utilization of the constant energy source by the cyclical energy demand. Less expensive energy storage means (heated ponds, aquifers), when they become fully characterized, will allow even more cost-competitive systems. Extensive design tradeoff studies have been performed for the example site, Intalco Aluminum Corporation and the surrounding communities of Ferndale and Bellingham, Washington. These tradeoff studies indicate that a heating demand equivalent to 12,000 single-family residences can be supplied by the energy from the Intalco site. Using a .30-year payback criterion (consistent with utility planning practice), the average cost of energy supplied over the system useful life is predicted at one-third the average cost of fossil fuel Close

• 5. [Image] Improving salmon passage: draft, the Lower Snake River juvenile salmon migration feasibility report/environmental impact statement

  	The purpose of this summary report is to provide an overview of the findings developed for the Lower Snake River Juvenile Salmon Migration Feasibility Study. For more detailed information, the reader should ...
  	Citation × Citation Citation Abstract Copy Title: Improving salmon passage: draft, the Lower Snake River juvenile salmon migration feasibility report/environmental impact statement Year: 1999, 2004 The purpose of this summary report is to provide an overview of the findings developed for the Lower Snake River Juvenile Salmon Migration Feasibility Study. For more detailed information, the reader should refer to the Draft Feasibility Report/Environmental Impact Statement and attached appendices. The genesis of this study is the National Marine Fisheries Service's 1995 Biological Opinion for the Reinitiation of Consultation on 1994-1998 Operation of the Federal Columbia River Power System and Juvenile Transportation Program in 1995 and Future Years (95 Biological Opinion). While the focus of this study is the relationship between the four dams on the lower Snake River and their effects on juvenile fish traveling toward the ocean, the implications of the study are broader. The Draft Feasibility Report/Environmental Impact Statement includes the best available information on the biological effectiveness, engineering, economic effects, and other environmental effects associated with the four specific alternatives. It does not, however, include a recommendation or identify a preferred alternative. This will give the public and other agencies an opportunity to review and understand this information and provide input before a preferred alternative is selected. At the same time, this will allow the region to consider the Habitat, Hatcheries, Harvest, and Hydropower Working Paper on salmon recovery by the Federal Caucus. Information from this process will be fully examined to determine how it may influence decisions on actions for the lower Snake River. Title: Improving salmon passage: draft, the Lower Snake River juvenile salmon migration feasibility report/environmental impact statement Year: 1999, 2004 The purpose of this summary report is to provide an overview of the findings developed for the Lower Snake River Juvenile Salmon Migration Feasibility Study. For more detailed information, the reader should refer to the Draft Feasibility Report/Environmental Impact Statement and attached appendices. The genesis of this study is the National Marine Fisheries Service's 1995 Biological Opinion for the Reinitiation of Consultation on 1994-1998 Operation of the Federal Columbia River Power System and Juvenile Transportation Program in 1995 and Future Years (95 Biological Opinion). While the focus of this study is the relationship between the four dams on the lower Snake River and their effects on juvenile fish traveling toward the ocean, the implications of the study are broader. The Draft Feasibility Report/Environmental Impact Statement includes the best available information on the biological effectiveness, engineering, economic effects, and other environmental effects associated with the four specific alternatives. It does not, however, include a recommendation or identify a preferred alternative. This will give the public and other agencies an opportunity to review and understand this information and provide input before a preferred alternative is selected. At the same time, this will allow the region to consider the Habitat, Hatcheries, Harvest, and Hydropower Working Paper on salmon recovery by the Federal Caucus. Information from this process will be fully examined to determine how it may influence decisions on actions for the lower Snake River. Close

• 6. [Image] The Third Klamath Basin Watershed Restoration and Research Conference

  	Cover title; "March 1999."
  	Citation × Citation Citation Abstract Copy Title: The Third Klamath Basin Watershed Restoration and Research Conference Year: 1999, 2004 Cover title; "March 1999." Title: The Third Klamath Basin Watershed Restoration and Research Conference Year: 1999, 2004 Cover title; "March 1999." Close

• 7. [Image] Seeking refuge: making space for migratory waterfowl and wetlands along the Pacific Flyway

  	Abstract "Seeking Refuge" examines the history of migratory waterfowl management along the Pacific Flyway, the westernmost of four main migration routes in North America. Drawing on approaches from historical ...
  	Citation × Citation Citation Abstract Copy Title: Seeking refuge: making space for migratory waterfowl and wetlands along the Pacific Flyway Author: Wilson, Robert Michael Year: 2003, 2005, 2004 Abstract "Seeking Refuge" examines the history of migratory waterfowl management along the Pacific Flyway, the westernmost of four main migration routes in North America. Drawing on approaches from historical geography and environmental history, this study shows how wildlife officials developed migratory bird refuges in Oregon and California, where over 60 percent of Pacific Flyway waterfowl winter. During the early-twentieth century, reclamation and river diking eliminated most of the wetlands in the birds' wintering range. Bird enthusiasts such as bird watchers and duck hunters successfully lobbied for the creation of wildlife refuges in a few areas along the flyway. These early refuges failed to protect waterfowl habitat and they were severely degraded by reclamation. In the 1930s and 1940s, the U.S. Fish and Wildlife Service (FWS) and its predecessor, the Bureau of Biological Survey, undertook an ambitious program to resurrect these sanctuaries and to create new ones. Many farmers opposed these refuges out of fear that waterfowl would damage crops. To respond to these concerns and to ensure an adequate food supply for the birds, the FWS raised rice, barley, and other grains. The agency adopted many of the technologies of modern, industrial agriculture including synthetic herbicides and insecticides such as 2, 4-D and DDT. By the 1960s, the refuges had become largely mirrors of the surrounding irrigated farmlands, the main difference being that the FWS raised grain for waterfowl rather than for market. Refuges could not escape the agricultural settings in which they were embedded. As units within the irrigated countryside, Pacific Flyway refuges were often at the mercy of nearby farmers and federal reclamation agencies. Poor water quality and insufficient supplies of water often hampered FWS efforts to manage refuges. In the late-twentieth century, reduced water supply due to diversions to California municipalities and to sustain endangered fish species affected the amount of water reaching refuges. This dissertation has other goals. First, it critiques the anthropocentrism of most historical geography by focusing on how political, cultural, and ecological factors affected wildlife. Second, it contributes to the literature on the state's role in environmental protection by investigating the overlapping, and often contradictory, spaces within which wildlife managers implemented environmental regulations. Title: Seeking refuge: making space for migratory waterfowl and wetlands along the Pacific Flyway Author: Wilson, Robert Michael Year: 2003, 2005, 2004 Abstract "Seeking Refuge" examines the history of migratory waterfowl management along the Pacific Flyway, the westernmost of four main migration routes in North America. Drawing on approaches from historical geography and environmental history, this study shows how wildlife officials developed migratory bird refuges in Oregon and California, where over 60 percent of Pacific Flyway waterfowl winter. During the early-twentieth century, reclamation and river diking eliminated most of the wetlands in the birds' wintering range. Bird enthusiasts such as bird watchers and duck hunters successfully lobbied for the creation of wildlife refuges in a few areas along the flyway. These early refuges failed to protect waterfowl habitat and they were severely degraded by reclamation. In the 1930s and 1940s, the U.S. Fish and Wildlife Service (FWS) and its predecessor, the Bureau of Biological Survey, undertook an ambitious program to resurrect these sanctuaries and to create new ones. Many farmers opposed these refuges out of fear that waterfowl would damage crops. To respond to these concerns and to ensure an adequate food supply for the birds, the FWS raised rice, barley, and other grains. The agency adopted many of the technologies of modern, industrial agriculture including synthetic herbicides and insecticides such as 2, 4-D and DDT. By the 1960s, the refuges had become largely mirrors of the surrounding irrigated farmlands, the main difference being that the FWS raised grain for waterfowl rather than for market. Refuges could not escape the agricultural settings in which they were embedded. As units within the irrigated countryside, Pacific Flyway refuges were often at the mercy of nearby farmers and federal reclamation agencies. Poor water quality and insufficient supplies of water often hampered FWS efforts to manage refuges. In the late-twentieth century, reduced water supply due to diversions to California municipalities and to sustain endangered fish species affected the amount of water reaching refuges. This dissertation has other goals. First, it critiques the anthropocentrism of most historical geography by focusing on how political, cultural, and ecological factors affected wildlife. Second, it contributes to the literature on the state's role in environmental protection by investigating the overlapping, and often contradictory, spaces within which wildlife managers implemented environmental regulations. Close

• 8. [Image] The Endangered Species Act and its impact on agricultural producers: hearing before the Subcommittee on Conservation, Credit, Rural Development, and Research of the Committee on Agriculture, House of representatives, One Hundred Eighth Congress, second session, July 26, 2004, Greely, CO.

  	CONTENTS Lucas, Hon. Frank, a Representative in Congress from the State of Oklahoma, opening statement .................................................................................... 1 Musgrave, ...
  	Citation × Citation Citation Abstract Copy Title: The Endangered Species Act and its impact on agricultural producers: hearing before the Subcommittee on Conservation, Credit, Rural Development, and Research of the Committee on Agriculture, House of representatives, One Hundred Eighth Congress, second session, July 26, 2004, Greely, CO. Author: United States. Congress. House. Committee on Agriculture. Subcommittee on Conservation, Credit, Rural Development, and Research. Year: 2004, 2005 CONTENTS Lucas, Hon. Frank, a Representative in Congress from the State of Oklahoma, opening statement .................................................................................... 1 Musgrave, Hon. Marilyn N., a Representative in Congress from the State of Colorado, opening statement........................................................................... 2 Witnesses Foutz, Alan, president, Colorado Farm Bureau, Centennial, CO ........................ 10 Prepared statement .......................................................................................... 38 George, Russell, executive director, Colorado Department of Natural Resources, Denver, CO............................................................................................. 4 Prepared statement .......................................................................................... 29 Palmer, William, executive director, Rocky Mountain Bird Observatory, Brighton, CO ........................................................................................................ 16 Prepared statement.......................................................................................... 60 Sims, James T., executive director, Western Business Roundtable, Golden, CO.......................................................................................................................... 13 Prepared statement .......................................................................................... 43 Stetson, Jean, co-chairman, Endangered Species Committee, Colorado Cattlemen, Craig, CO..................................................................................................... 7 Prepared statement .......................................................................................... 36 Submitted Material Weege, Merle, secretary, Ginseng Board of Wisconsin, statement...................... 65 Title: The Endangered Species Act and its impact on agricultural producers: hearing before the Subcommittee on Conservation, Credit, Rural Development, and Research of the Committee on Agriculture, House of representatives, One Hundred Eighth Congress, second session, July 26, 2004, Greely, CO. Author: United States. Congress. House. Committee on Agriculture. Subcommittee on Conservation, Credit, Rural Development, and Research. Year: 2004, 2005 CONTENTS Lucas, Hon. Frank, a Representative in Congress from the State of Oklahoma, opening statement .................................................................................... 1 Musgrave, Hon. Marilyn N., a Representative in Congress from the State of Colorado, opening statement........................................................................... 2 Witnesses Foutz, Alan, president, Colorado Farm Bureau, Centennial, CO ........................ 10 Prepared statement .......................................................................................... 38 George, Russell, executive director, Colorado Department of Natural Resources, Denver, CO............................................................................................. 4 Prepared statement .......................................................................................... 29 Palmer, William, executive director, Rocky Mountain Bird Observatory, Brighton, CO ........................................................................................................ 16 Prepared statement.......................................................................................... 60 Sims, James T., executive director, Western Business Roundtable, Golden, CO.......................................................................................................................... 13 Prepared statement .......................................................................................... 43 Stetson, Jean, co-chairman, Endangered Species Committee, Colorado Cattlemen, Craig, CO..................................................................................................... 7 Prepared statement .......................................................................................... 36 Submitted Material Weege, Merle, secretary, Ginseng Board of Wisconsin, statement...................... 65 Close

• 9. [Image] Research information needs on terrestrial vertebrate species of the interior Columbia River basin and northern portions of the Klamath and Great basins: research, development, and application database

  	"September 1997"; Includes bibliographical references (p. 24)
  	Citation × Citation Citation Abstract Copy Title: Research information needs on terrestrial vertebrate species of the interior Columbia River basin and northern portions of the Klamath and Great basins: research, development, and application database Author: Marcot, Bruce G. Year: 1997, 2005, 2004 "September 1997"; Includes bibliographical references (p. 24) Title: Research information needs on terrestrial vertebrate species of the interior Columbia River basin and northern portions of the Klamath and Great basins: research, development, and application database Author: Marcot, Bruce G. Year: 1997, 2005, 2004 "September 1997"; Includes bibliographical references (p. 24) Close

• 10. [Image] Surveying forest streams for fish use

  	Oregon Department of Forestry Forest Practices Section 2600 State Street Salem, OR 97310 Dl Fish 8 Wildlife Oregon Department of Fish and Wildlife Habitat Conservation Division P. O. Box 59 Portland, OR ...
  	Citation × Citation Citation Abstract Copy Title: Surveying forest streams for fish use Author: Oregon. Forest Practices Section; Oregon. Habitat Conservation Division Year: 1995, 2005, 2004 Oregon Department of Forestry Forest Practices Section 2600 State Street Salem, OR 97310 Dl Fish 8 Wildlife Oregon Department of Fish and Wildlife Habitat Conservation Division P. O. Box 59 Portland, OR 97207 Introduction Identifying Oregon streams that contain fish is an important part in carrying out the new Water Protection Rules. These rules aim to protect areas of benefi-cial uses, such as fish. First, however, the beneficial uses present in each forest stream must be correctly identified. At present, a large number of fish- bearing streams are not identified on stream classification maps. To correct this problem, the Oregon Department of Forestry ( ODF) and the Oregon Department of Fish and Wildlife ( ODFW) must complete comprehensive surveys to identify fish use on all non- federal forest streams in Oregon. This effort will require at least 3 to 5 years and a significant financial investment. Because many streams are not accurately classified, the new rules also tempo-rarily protect streams that are likely to contain fish. Under the rules, for example, if Stream A flows into a body of water known to contain fish, it is assumed that fish also are using Stream A, up to the point that a natural barrier blocks their way farther upstream ( see OAR 629- 57- 2100: ll( b) B). Once the survey efforts are complete, this interim rule will not be needed. Coordinated efforts by public agencies, landowners, and others to complete fish- presence surveys will assure that important fisheries resources are pro-tected in the most cost- effective way. Landowners or any interested party may collect stream- classification information so that the overall survey can be completed as quickly as possible. Many private forest landowners, in cooperation with Oregon Department of Fish and Wildlife, are now completing inventories of stream habitat conditions on their lands. In the future, these cooperative efforts may also include fish-presence surveys. This publication tells how to complete fish- presence surveys on forested streams. The guidelines cover: How to plan either " operation- specific" or " maximum upstream fish distribution" surveys The proper way to conduct surveys The proper time of year to conduct surveys Minimum efforts required in completing the surveys The legal requirements for completing the surveys How to provide information to Oregon Department of Forestry to update the stream classification maps The stream reclassification process Operation- specif ic surveys Maximum upstream distribution surveys Planning the survey There are two major types of survey: operation- specific surveys, and surveys to find the maximum upstream distribution of fish. Each type requires different planning and is conducted using different approaches. Operation- specific surveys are those to classify a stream only in the particular area of an operation. This kind of survey may not include efforts to determine the maximum upstream extent of fish use. An operation- specific survey takes minimal planning and coordination. However, it may be very inefficient in the long run because future activities in other areas of the stream may require additional surveys. An operation- specilk survey is very simple to complete. It starts at the down-stream end of the operation area and moves upstream either to the end of the operation area or to the end of fish distribution, whichever comes first. If the purpose of the survey is to prove no fish use, the surveyor must be sure to make at least the minimum effort required to find fish ( see the section on " Survey Effort" on page 10). This kind of survey is done on an entire stream reach or on multiple stream reaches rather than on a restricted portion of a stream. Often, all streams within a basin or reach are completely surveyed. In some cases, the surveys encompass entire ownerships or watersheds. The specific locations of planned operations are usually not the main factor in setting up this kind of survey but can help decide which areas to survey first. Surveys to find the maximum upstream extent of fish use may be the most efficient and cost- effective. Surveyors often cover a group of streams in one area at a time; therefore, travel time is minimized because, often, a group of streams can be easily reached by one common forest road. When travel time is less, the time spent actually completing surveys is greater. This kind of survey may require slightly more planning and coordination to assure efficiency and to minimize duplication of effort by adjacent landowners or by other public agencies, but overall this approach is more cost- effective than the operation-specific surveys. Surveying for the maximum upstream distribution of fish may take more plan-ning than an operation- specific survey, but it is still relatively simple. First, look at ODF Stream Classification Maps for the survey area to see the current extent of fish- use streams. Also note which streams are not classified at all. Next, decide where to start the survey. It may help your planning if you know the relationship between watershed basin area and fish use for your area. Contact the local ODFW office to find out whether these relationships have been established for streams in your area. The information predicts where fish use is " likely to end" and so will help you decide where to start your surveys. At this point, you also may want to consider operations that are planned for certain areas and decide to survey those areas first. After choosing a starting area, look at current road maps to find potential starting points for the survey ( see Figure 1). Look for access points ( such as road crossings) near the upper reaches of the stream. When possible, a survey should start near the highest accessible point in the watershed. If road access to the stream is limited, you may want to start the survey near the point at which the stream's classification size changes from " medium" to " small"; often this point is near the end of fish use ( see Figure 2, page 4). At the starting point, first sample upstream. If you find fish, continue the survey upstream until fish use ends. Be sure to continue sampling above the point at which fish use ends ( see " Survey Effort," page 10). If you make all the required efforts but do not find fish, then survey downstream from the original starting point until you find fish. When surveying downstream, it is important to walk on the streambank until you are ready to sample so that the water stays clear. Begin fish survey above road crossing Fish use extends at least this far Figure I . Selecting survey starting points in an area with a road crossing. Additional survey work may be required if the maximum distribution of fish seems to be affected by a road culvert. If the stream above the culvert has no fish, sample the pool immediately below the culvert. If you find fish in this pool or downstream near the culvert, the culvert is a possible barrier to fish passage. Describe the culvert and the stream on the survey form ( page 19). If you do not find fish in the pool below the culvert, continue the survey down-stream until you do see fish. Begin fish survey here \ \\ \ / I Fish use extends at least this far - - k I Figure 2. Selecting survey starting points, based on the stream- size classification, in an area without a road crossing. Surveys to find the maximum upstream distribution of fish may require sampling across several land ownerships. Be certain to get permission from other landowners before beginning the survey. Contacts with other landowners are also important to prevent a duplication of effort, because many landowners and agencies may be conducting fish- presence surveys. When figuring how many surveyors and how much time you'll need to com-plete surveys in your area, you may want to consider the Department of Forestry's experience. We found that sampling a township ( 36 square miles) required approximately 24 person- days in the Coast region, but an area the same size in the Blue Mountains required only 4 person- days. Survey methods The accuracy and reliability of survey results depend greatly on the methods used to conduct the survey. Methods range from simply looking in the stream ( visual observation) to more intensive and effective sampling with a backpack electroshocker. The method you choose depends on the availability of sam-pling equipment, the size of the stream, the flow and clarity of the water, and other factors. It is important to select a sampling method that is best for the type of survey and for the waters being sampled. If the sample method is not appropriate, the results of the survey will not be very useful. For example, just looking at a stream may tell you there are fish in it at that point, but it is not an acceptable way to find the maximum upstream extent of fish use. Surveys to show that fish are not present require more sampling and specialized equipment in order to provide reliable results. Whenever the survey uses methods other than an electroshocker, it's important to thoroughly explain on the survey report form the reasons for using the other methods. This is the simplest method; it involves only walking the stream to look for fish. It is best to wear polarized sunglasses to reduce glare from the water and to survey only when water conditions allow good visibility. It's also best to walk upstream so that you can " sneak up" on fish in pools. Fish often are near the upstream ends of pools waiting for food to drift toward them. Small fish, such as fry, often are in shallow water along the margin of the stream. Be very alert because fish usually will dart into cover when they detect any movement, especially in small headwater streams. It helps to toss bread crumbs, insects, small twigs, or bemes into the stream to entice the fish to leave cover. The visual method is best suited to small streams where pools aren't deep enough to prevent your seeing the fish. This method is also the least damaging to the fish because actual collection is not required. However, the value of survey results can be reduced by many factors such as cloudy water, surface glare on the water, overcast days ( reduced light), fish behavior, and even the surveyor's poor eyesight. For these reasons, this method is not effective for determining the maximum upstream limit of fish distribution, although it can be used to prove fish are in a certain reach of the stream. Snorkeling is a special method of visual observation that can work well in some situations. Snorkeling allows you to see underwater through a diving mask and breathing snorkel. This method can be used in larger waters where electroshockers are less successful, and it has been used to locate fry where other methods failed. Night snorkel surveys are particularly useful for observ-ing bull trout fry. Visual observation Hook and line Backpack electroshocker The hook- and- line method uses a rod and reel and relies on the feeding be-havior of the fish. In small streams, drop a baited hook into the deepest pools, where larger fish often are. Bait can include worms, single eggs, cheese, dry flies, or stream insects such as caddis larvae. Sample pools that have a lot of cover because those tend to support greater numbers of fish. As with the visual observation method, approach the pool cautiously to avoid alerting the fish. To minimize the risk of injuring or killing the fish, always use barbless hooks. The hook- and- line method can be used when conditions are not good for visual sampling; for example, when water is not clear, flow is high, or the day is overcast. This method may be the most effective for sampling some larger or deeper waters where visual and electroshocker methods can be ineffective. These waters include deep beaver ponds and large, steep streams where downstream barriers ( such as falls and very steep sections) keep fish out of the small tributaries. This method has limitations, though, depending on fish behavior and the life stage of the fish that are present. Fish may be reluctant to bite on cold days, or when the water is murky with sediment, or if the fish detect the surveyor's presence. Also, hook- and- line sampling is not effective if only fry are in the stream. This method also depends on the angling skills of the surveyor. As with the visual observation method, hook- and- line sampling may not be the best way to determine the maximum upstream distribution of fish in small streams, but often it can be used to find fish in larger waters. The most effective way to determine the upstream extent of fish is with a backpack electroshocker. Electroshocker sampling requires additional training and experience, though, to be effective and safe. A backpack electroshocker introduces an electric field into the stream that temporarily immobilizes fish. Stunned fish can be observed as they float in the water, or they can be captured in a small hand net for closer observation if necessary. As with other methods, it is best to work in an upstream direction, wear polarized glasses, and to approach the sampling site carefully to avoid alerting the fish. One person nets fish while another person operates the electroshocker. The netter should walk behind or beside the shocker to avoid alerting the fish. The electroshocker can be very effective for sampling in small streams even where brush or instream cover prevents most other sampling methods. In fact, an electroshocker is often most effective in areas with instream cover because fish usually concentrate in these locations. This method works in streams of various sizes but is less effective in larger streams and in deep pools, espe-cially large beaver ponds. Use electroshockers carefully to minimize killing fish. When properly adjusted and used, the electroshocker should stun the fish without killing them. The fish may escape if the current is set too low, but usually the surveyor will still see the fish and so be able to document fish presence. To sample effectively and minimize fish kill, set the electroshocker on the lowest practical voltage output and low- frequency currents ( low pulse rates). Before sampling, use a voltame-ter to test the electroshocker in a stream. If the voltameter is not available, it is a good idea to test the electroshocker in a stream that you know has fish before working in streams whose fish use you do not know. The test will tell you whether the equipment is working and the effects of using different settings. The surveyors' safety must be considered carefully before using this method. Electroshockers can injure or kill humans if not properly used. Surveyors should not use this method without proper training, including CPR training. Surveyors should work in crews of at least two. All surveyors should wear rubber waders and rubber gloves during stream shocking and never use dipnets with metallic handles; the nets should have wood or fiberglass handles. All members of an electroshocking crew should understand the proper operation procedures and potential dangers of this equipment. The effectiveness of electroshocker sampling depends on water conditions and on the skills of the electroshocker operator and the netter. The electroshocker method may not be so useful in high flows or in turbulent or murky water because the surveyors may not see immobilized fish. Another drawback to this method is that the electroshockers may not be widely available and can be expensive. However, with proper training and experience and under suitable survey conditions, this method is the best for accurately determining the maximum upstream extent of fish use. There may be situations where reliable results can be had by using methods not discussed here. For example, headwater beaver ponds may be effectively Other methods sampled by fishing for at least 48 hours with minnow traps baited with salmon eggs or commercial trout bait. Or, seine nets may be effective in beaver ponds or larger waters. If you are thinking about using these or other sampling methods, discuss it first with the departments of Fish and Wildlife and of Forestry. They will decide whether the proposed methods are appropriate and, if so, set the required minimum level of sample effort for the alternate method. A backpack electroshocker is the best way to get reliable information about the upstream extent of fish use or to prove a stream is m e N ( no fish use). Sur- Survey methods: vey data that document the presence of fish through other methods, such as a summary visual observation or hook- and- line, will always be used to classify streams as Type F as far up as the point of observation, even though the exact upstream extent of fish use may not be known. In some cases, methods other than an electroshocker may give reliable information about the maximum upstream distribution of fish. Examples include deep beaver ponds and large, steep streams in which barriers keep fish out of small upstream tributaries. In those cases, reliable results may be better obtained with hook- and- line sampling or with other methods. Whenever the survey is conducted by methods other than an electroshocker, the reasons for choosing the other method must be thor-oughly explained on the survey form. Timing the surveys Survey accuracy depends a lot on the time of year the survey is done and on stream conditions at that time. Since the purpose of the survey is to accurately document the presence or absence of fish, it is critical to do the survey when fish are expected to be using the upper reaches of a stream. This generally is near spawning times or soon after fry emerge, when stream flows are relatively high. A survey done during a low- flow period may not indicate the actual maximum upstream extent of fish use or accurately prove no fish use the stream. Fish may use the upper reaches of a stream for a limited time only, so fish- use surveys must be timed carefully. Surveys done at other than recommended times may not give a complete description of fish use. For example, if fish are found at other than the recommended survey times, the surveyed part of the stream can be classified as fish- bearing, but the maximum upstream extent of fish use may not be known. If fish are not found, that will not necessarily prove that the stream reach does not support fish use. Only if the survey is made at a time when fish are most likely to be there can the absence of fish be a reliable sign that no fish use that portion of the stream. Other factors can affect the reliability of the survey even if it is made at the proper time. Abnormal flows due to drought or extreme runoff could affect the distribution of fish or the sampling efficiency of the surveyor. So, it is best not only to do the sampling within the recommended time period but also when conditions are appropriate. In some cases, survey timing may not have much effect on the reliability of survey results. This could occur when factors other than seasonal flow patterns control the upstream extent of fish distribution. For example, streams that get most of their water from springs may not have seasonal flow variations, including summer flows low enough to control the upstream distribution of fish. Or, conditions other than low flow could be controlling distribution. For example, large, steep streams that have natural barriers such as falls and steep, impassable sections. In such cases, surveys taken outside the recommended time periods may yield reliable data. However, it is important to describe these conditions thoroughly on the survey forms to justify not following the recom-mended timing. See Table 1 for the recommended sampling periods for different regions of the state for normal water- flow years. Periods differ due to variations in stream flow patterns, fish species, and life- history traits of the species in the different areas. Contact the local ODFW office before sampling to find out the best time to survey the stream you are planning to sample. Table 1. General recommended time periods to sample streams, by geographic region, during nomull water- flow years. Please contact your local ODFW ofice before sampling in order to get specific timing recommendations for the stream you will be sampling. REGION of Recommended Georeaion Stream Survey Period WESTERNO REGON All Coast South Coast West Cascades Interior Siskiyou March 1 through May 3 1 EASTERONR EGON All except spring- fed April 1 East Cascades through June 30 Blue Mountains Spring- fed streams* Entire year * Spring- fed streams are streams that get most of their water Born groundwater sources and that have very minor seasonal variations in flow. Stream surveys must be done within certain time periods ( Table 1) if the purpose is to prove the stream does not contain fish or to document the maximum upstream extent of fish use. mming recommendations are based on normal water- flow years and may vary in some years. Contact the local ODFW office before sampling to get specific timing recommendations for the streams to be surveyed. Information gathered at other times of the year may be used to document fish presence but may not be reliable enough to establish upstream fish- use limits or to classify the stream as II) lpe N ( no fish use). Whenever the recommended survey timing is not used, it is important to explain the reasons on the survey form so that the data can be evaluated for reliability. ~ - ~ Survey timing: a summary Survey effort: a summary Survey effort The level of effort used to complete the survey also can affect the reliability of the survey results. If the level of effort or the amount of stream sampled is too little, it may be wrong to conclude that fish are not present. The following guidelines describe the minimum level of survey effort required to assure that the data are reliable. If the purpose of the survey is to show that no fish use the stream, the survey will be considered reliable only if it includes at least 50 yards of stream length md a minimum of six pools, each at least 1 foot deep, immediately upstream of the point at which the non- fish- bearing section begins. ( In some cases, the survey will have to cover much more than 50 yards of stream in order to also include the required six pools.) In addition, the survey must include sampling any beaver dam ponds in the upstream non- fish section. Surveyors are encouraged to exceed the minimum level of effort in order to be even more sure that fish are absent from a stream reach and that the maximum upstream extent of fish use has been found. A survey intended to show the absence of fish must sample at least 50 yards of stream distance and a minimum of six pools, each at least 1 foot deep, imme-diately upstream of the point at which fish use is believed to end. In addition, any beaver ponds upstream must be sampled as part of the survey. The require-ments for the methods used and the timing of the survey also must be met in order to document the absence of fish. Legal requirements In Oregon, the Department of Fish and Wildlife regulates the collection of fish for personal or scientific use. Generally, collection methods prohibited by the general angling regulations, such as electroshockers, traps, or nets, and collec-tions at times of the year when angling is closed will require a Scientific Collection Permit from the Oregon Department of Fish and Wildlife. Scientific Collection Permits can be issued to agencies, companies, or indi-viduals. Request an application from the Fish Division of the Oregon Depart-ment of Fish and Wildlife, P. O. Box 59, Portland, OR 97207; telephone ( 503) 229- 5410, extension 323. Submit the application at least 1 month before you plan to do the survey in order to be sure the permit can be issued in time. The application requests information about the collection method to be used, when and where collection will be made, and a summary of the proposed project. By law, surveyers must keep records of their collection activities and submit them to the Oregon Department of Fish and Wildlife. Surveys using the visual observation method ( including snorkeling) do not require any licenses or permits because fish are not physically collected. Sampling with the hook- and- line method during open fishing seasons requires only a valid angling license. However, Oregon resident landowners and their immediate families do not need angling licenses to fish on land they own and live on. In either case, the general ahgling regulations for the stream must be followed during hook- and- line sampling unless a Scientific Collection Permit is obtained. Additional restrictions on survey efforts may apply if the stream contains species that the state or federal government lists as sensitive, threatened, or endangered species. Please contact your local ODFW office to find out whether any of these species are likely to be in streams you plan to sample. Reporting survey results Give survey data to the local ODF district office so that district Stream Classi-fication Maps can be updated. On page 19 is a blank survey report form. It asks for information about the location of the stream; the methods, timing, and effort of the survey; the physical character of the stream; observations of fish and wildlife; and the presence of natural or human- created barriers to fish passage. complete one form for each stream reach where fish were ob-served or fish use was found to end. See Figure 3 ( page 12) for descriptions of some fish species common to $ mall, forested streams; these may help to identify fish seen during surveys. Detailed instructions for completing the survey form are on pages 14 through 18. Attach to the Fish Presence Survey Form a copy of the ODF Stream ClassM-cation Map for the surveyed area or, if that is not available, a copy of the 7.5 minute USGS topographic map for the area. Note the following information on the map. ( Examples of completed survey report forms and maps are on pages 21 through 30.) The area of the stream that was actually surveyed ( including the areas without fish) as part of the survey effort. Highlight in yellow the entire stream reach surveyed ( see examples on pages 25,28, and 30). The upper limit of fish use. Note this on the map by drawing a line across the stream and writing the letter F at that point. The name of the surveyor. The date the stream was surveyed. GENUS ONCORHYNCUS - PACIFIC SALMON IOENTIFICATION FEATURES OF JUVENILES Faint parr marks. extend little. if am: below latanl line. Lures SOCKEYE w GENUS ONCORHYNCUS- TROUT IDENTIFICATIOEI FUTURES OF JUVENILES pols in dorsal Teeth on of tongue Maxillary extend past rear margin on throat W - Of eye CUTTHROAT 5 - I 0 parr marks on ridge ahead of dorsal tongue astend & st rear mark on throat Y; V margin of eye STEELHEAD- RAINBOW Few or no spots i n tail Figure 3. Identification characteristics of some juvenile salmon and trout species that may be observed in forested streams. 3. Permission to enter private forest lands should be obtained from all land-owners before the surveys are conducted. 4. Fish- presence surveys should then be made according to the guidelines given in this publication. 5. The required survey information, recorded on the Fish Presence Survey Form and maps, should be given to the local ODF district office. 6. The ODF office will give copies of the completed survey forms and maps to the local office of the Oregon Department of Fish and Wildlife. 7. The Department of Forestry will review the information, usually in consul-tation with the Oregon Department of Fish and Wildlife, to determine whether the survey results are reliable. 8. Based on its assessment of data reliability, the Department of Forestry will make appropriate changes to the ODF Stream Classification Maps. 9. All affected landowners will be notified of the proposed stream classifica-tion changes, according to the notification rules ( OAR 629- 57- 2110( 2)). Instructions for completing the survey report form The following information should be reported on the Fish Presence Survey Form. These instructions are in the order that the information appears on the form. Complete one form for each stream reach or branch where fish were observed or fish use was found to end. This may require assigning codes to unnamed tributaries ( for example, " trib. a," " trib. b") so that survey data can be cross- referenced to the survey maps. Please refer to examples on pages 21 through 29. Surveyor Narne( s): The name of the person or persons responsible for con-ducting the survey and reporting the results. AgencyfCompany: The name of the agency or company that employs the surveyor ( if applicable). Landowner: The name of the landowner of the reach surveyed. Mailing Address and Phone: The address and phone number for the person responsible for the survey. Stream: The name of the stream as reported on the USGS or ODF Stream Classification Map for the area. If the stream is unnamed, report the stream as " unnamed" and list the tributary that it flows into (" Tributary to..."). Tributary to: The name of the main stream ( as reported on the USGS or ODF map) that the surveyed stream flows into. This is especially important if the surveyed stream is unnamed. Quad Map: The name of the USGS 7.5 minute topographic map that includes the reach of the stream surveyed. If the surveyed reach covers more than one quad map, report first the name of the map that shows the identified end- point of fish use and then give the other maps' names. Location: A legal description ( township, range, and section to at least the quarter section) of the location where fish use ends. Date Surveyed: The month, day, and year the fish survey was conducted. Survey Method: Check the box for the survey method used. If more than one method was used, check all that apply and note the most often used method in the comments section or in the form's margin. Survey Amount Above End of Fish Use: The length of stream reach that was surveyed immediately upstream of the identified end of fish use. Estimate ( in feet) the length surveyed, and give the number of pools sampled for fish in that section. A survey to prove the absence of fish must sample at least 50 yards of stream and at least six pools immediately upstream of the end of fish use. In addition, any upstream beaver ponds must also be sampled. Flow Level: The flow conditions at the time of the survey. Use the following categories of flow. Low: Ranges from a series of isolated pools to flowing across less than 75 percent of the average bankfull width. Moderate: Surface water is flowing across 75 to 90 percent of the average bankfull width. High: Surface water flowing across more than 90 percent of the average bankfull width. It is not recommended thatfih presence surveys be conducted at high jlows. Weather: The weather during most of the fish survey ( rainy, overcast, partly cloudy, sunny, snowy, etc.). Water Clarity: The water visibility during the survey. Use the following categories of water visibility. Clear: Visibility is good in pools, deep pools, and riffles. Moderate: Visibility is good only in riffles and shallow pools. Turbid: Visibility is poor in both riffles and pools. It is not recommended that fih presence surveys be conducted when water is turbid. Water Temperature ( optional): The temperature of the stream ( in degrees Farenheit) at the time of the survey. Fish observations Report the species and approximate size ranges of fish observed in the sur-veyed reach. Use Figure 3 ( page 12) as a guide to identifying some game fish species commonly found in small, forested streams. Use the following codes and instructions to complete this section. Species: Use the following names or codes to report fish observed during the survey. If you observe a species not listed here, such as Pacific lamprey, use its common name. Name Species Code Coho salmon Co Cutthroat trout Ct Rainbow troutfsteelhead Rb/ St Bull trout BUT Brook trout BT Unknown salmonid UnS Sizes: Report the size range of fish, in inches, by species. For example, the size range of coho observed could be reported as " 1- 4 inches." If you see several sizes of one species ( for example, some cutthroat trout in the " 1- to 2- inch range and others in the " 6- to 8- inch" range), list them separately. Aquatic wildlife The types of aquatic wildlife that may be observed include tailed frogs ( includ-ing juvenile " tadpoles"), Pacific giant salamanders, and Olympic salamanders. Species: Give the common name of the species, if known. If you don't know the species name, at least report observations by a general name such as " salamanders." Number: The number of aquatic wildlife in each species or group observed. Physical stream data Report the physical characteristics of the stream in the vicinity of the end- point of fish use. Report information separately for ( 1) the section immediately at and downstream of the end of fish use, and ( 2) the area upstream of the maximum extent of fish use. Following are specific instructions for collecting this information. Bankfull Channel Width: By eye, estimate the average width ( in feet) of the bankfull channel for the 100- foot sections above and below the end- point of fish use. The bankfull channel is the area that is scoured by water during average high flows. The edge of the bankfull channel can be identified by looking for changes in vegetation, in soils and litter characteristics, or in the shape of the bank. The bank often will abruptly change slope at the bankfull boundary. Vegetation at the boundary often changes from annual vegetation ( such as grasses) to more permanent vegetation such as trees and shrubs. Estimate the width across the channel between the edges of the bankfull level. Current Wetted Width: Visually estimate the average width ( in feet) of the channel that contains flow ( is wetted) at the time of the survey. Report the estimated averages for the 100- foot sections above and below the end of fish use. Channel Gradient: Measure the average stream gradient with a clinometer for the 100- foot sections above and below the end of fish use. me a piece of flagging at eye level on a branch or shrub, walk up or down the stream bank, and then use the clinometer to sight on the flagging while you are standing on the channel bottom. Read and report the percent gradient. ODF Stream Class Size: The stream size (" small," " medium," or " large") from the ODF Stream Classification Maps for the reaches immediately above and downstream of the end of fish use. Natural barriers This information is very important for understanding relationships between the presence of fish and the physical characteristics of the stream. Understanding these relationships can help determine where fish- presence surveys should be concentrated and help predict where fish are likely to occur if survey informa-tion is not yet available. Generally, natural barriers are permanent structures such as falls or vertical drops more than 8 to 10 feet high for salmon or steel-head or 4 feet high for trout. Log jams, drops over logs, beaver dams, or other organic structures generally are only temporary barriers to fish passage, but report them as well. If fish use ends at a natural barrier, such as a waterfall, bedrock chute or cascades, describe the conditions at the site. Include a description of: ( 1) the type of barrier, ( 2) the approximate height ( in feet), ( 3) the percentage of slope, ( 4) the length ( in feet) of the bedrock chute or cascades, and ( 5) any other conditions that may be limiting fish passage. If the potential barrier is a bedrock chute, note whether the bedrock contains pools or rough features ( such as rocks, boulders, or other breaks in the flow), or whether the water flows in an even, shallow pattern over the bedrock. Please note on the survey map the locations of any natural barriers encountered. If you encounter a natural barrier, also be sure to sample above this point because fish often are found above natural barriers. Road- crossing barriers This information also is very important for understanding relationships be-tween the presence of fish and the physical characteristics of the stream. Road-crossing barriers can alter the relationships. If fish use ends at a road- crossing barrier, such as a culvert, describe the conditions at the site. Describe the type of barrier and its measurements at the time of the survey such as ( 1) the diameter of the culvert, in inches, ( 2) the depth ( in inches) of water in the culvert, ( 3) the height ( in feet) of the jump ( drop) below the culvert or structure, ( 4) the depth ( in inches or feet) of the plunge pool below the culvert outfall, ( 5) the gradient or slope of the culvert, given as a percentage as read off a clinometer, ( 6) the length ( in feet) of the culvert, and ( 7) any other factors that could affect fish passage. Please note on the survey map the locations of any road- crossing barriers, even if they are not at the end- point of fish use. As with natural barriers, be sure also to sample above the site because fish often are found above road- crossing barriers. Other comments Any other comments or notations that you think may be pertinent to the fish survey. It helps to describe any notable habitat characteristics, for example " lots of instream wood," " very few pools in the reach," " heavy silt load in the stream." Use the reverse side of the form if necessary. FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Surveyor Name( s): Agency: Land Owner: Mailing Address: Phone: Date Surveyed: Stream: Tributary to: Quad Map: Location: T R Sec. Survey Method ( d): 0 Electroshocker 0 h & g 0 Visual Survey Above End of Fish Use: Distance ( feet) Number of Pools Flow Level ( d): 0 Low 17 Moderate High Weather: Water Temperature: Water Clarity ( d): Clear 17 Moderate 17 Turbid FISH OBSERVATIONS AQUATIC WILDLIFE PHYSICAL STREAM DATA If fish use ends at a natural barrier, describe the conditions that prevent upstream fish passage. If fish use ends at a road crossing, describe conditions that may prevent upstream fish passage. Other comments ( use reverse side if necessary): FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Surveyor Name( s): . be Sorveq , 3 Troo+, FI s h G n r u l l , I*? , S.; L. Agency: N/ C I Land Owner: k! 4~ 4f, l T; M ~ C C Mailing address:?.^. sox ~ g~,\ L L I M UF~ A \ ID~ R) jC? suo Phone: BSB- 5555 ate surveyed: A p ( ; i 2 8, ! ?? s I Stream: Un hawed , " Tr I b R!' Tributary to: lr3 F . 21 o k so- ~ r a& QuadMap: D\ A &\ dy Location: T 305 R 5 " L Sec. 30, sw/ sto Survey Method ( d): d~ lectroshocker Angling 0 Visual Survey Above End of Fish Use: Distance ( feet) I 86 ' Number of Pools Flow Level ( d): CI Low cd~ oderate High Weather: S owv Water Temperature: 7 O F I Water Clarity ( V): dclear Moderate I7 Turbid FISH OBSERVATIONS AQUATIC WILDLIFE Species I Snes 1 Spedes 1 Quant'ity 1 PHYSICAL STREAM DATA If fish use ends at a natural barrier, describe the conditions that prevent upstream fish passage. bk If fish use ends at a road crossing, describe conditions that may prevent upstream fish passage. prf+ Other comments ( use reverse side if necessary): f- 15 L wsz ewd 30 $& abov e f *; rd John50~ m ain\ ifi< ~ r o s s i n OH ~ f r e a ~ 7.% ~ 5t redw g d ~ e n f & ry s t u p abde + he a d 4' & sh use - p & f i a n 10%. 2 1 OREGON FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Fish & Wildlife Stream: ~) nr? euce, d " Tr t b, O " Tributary to: w F & n~ oq CC. Quad Map: old &\ A% Location: T 382 R 5E Sec.' 30, si/ Sw I Survey Method ( 4): ~ lectroshocker 0 Angling 0 Visual Survey Above End of Fish Use: Distance ( feet) 2 5' 0 Number of Pools 20 Flow Level ( d): 0 Low d ~ o d e r a t e High Weather: Lw+ Water Temperature: 6 0 F I Water Clarity ( d): dclear Cl Moderate Turbid FISH OBSERVATIONS AQUATIC WILDLIFE Species 1 Snes I! , Species Quantity If fish use ends at a natural bamer, desc ' be the conditions that prevent u stre m fish assage. Fid - 4s 4+ 2 S ' ~ r t i Lm* r? d\. A dJ @ cater also % 15& 5 ( ho& a. r. rp Q5 W F - buffis @ ere fouu\ d . opstr + ye If fish use ehs) at a roa d. crossmng, descnbe conhlons that may prevent upstream fish passage. Other comments ( use reverse side if necessary): w tfw+ were fbU 4 above % z 6 + of (~ la+ erf~ ll above fu 25fcof I sowe years. 22 fail s& i ro fish t@ f& probab/ y vp FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP stream: V A ~ ~ ~ + SC~" T & ~ ributaryto: u. F. 3ehbtja14 Creek Quad Map: old - b a t d ~ Location: T 3 S 5 R 5 E Sec. Survey Method ( d): d~ lectroshocker 0 Anghng 0 Visual Survey Above End of Fish Use: Distance ( feet) a 2 5 Number of Pools 2 Flow Level ( d): 0 Low & oderate 0 High Weather: SvMwv Water Temperature: I Water Clarity ( d): d l e a r 0 Moderate 0 Turbid FISH OBSERVATIONS AQUATIC WILDLIFE - ... . .: : :....: ' ' . . . . . . A , , , .: . . . . , . . , .&& : ! Species ... . ..$ pedes Quantity PHYSICAL STREAM DATA If fish use ends at a natural barrier, describe the conditions that prevent upstream fish passage. M/ A If fish use ends at a road crossing, describe conditions that may prevent upstream fish passage. FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Stream: West h r k Aobrson Cr eeG Tributary to: Johnrow Cre~ k Quad Map: ( ~ ( 4Ith .\ Ay Location: T 385 R 5 E Sec. 2?,, 5E/ sLJ I Survey Method ( d): dlectroshocker 0 Angling Visual Survey Above End of Fish Use: Distance ( feet) 3 00 Number of Pools t% Flow Level ( V): 0 Low d ~ o d e r ae t High Weather: j , y~ I Water Temperature: 60" F= Water Clarity ( d): & ear Moderate Turbid FISH OBSERVATIONS AQ- U ATIC WILDLIFE t Spedes Quantity 1 I PHYSICAL STREAM DATA + IH n D CtsL 5h-* If fish use ends at a natural barrier, describe the conditions that prevent upstream fish passage. N I A If fish use ends t a roqj crossiy, describ~ concl~~ tohnats may prevent upstr am fish passa e. ~ hrvctr ert a no? pQ59 ~ c - r b LOWOJQ 4 u. 4 9 ) drop at * rut-/&. b l d a r p fn qr p aI . 7, slop is 6 70 , and w ( onp 7 % fu~ lv er+ 1s ~ chul~ ledb e replace4 t bi s Svmncr. Other comments ( use reverse s~ de~ fn ecessa ): Lower ~ t r c a - q r d r r & a & e + LC cd en. Sf- rm* bb; M Ieok 30a4, but + k shaln. dry up ;* SOW years. FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Mailing Address: ?. c, 3 2 , AJLO ~ L4- T o R 70 00 Phone: b40 - oool Date Surveyed: / Ha v 2 / cj? T I stream: ~ nnclcr- ed , " 7- r; b k " Tributary to: Lobs k c Creek Quad Map: BULL Lrceu Rtdqc Location: T 35 R 2W S ~ C . ~ ~ N € + 4 Survey Method ( d): ~ lectroshocker Angling 0 Visual Survey Above End of Fish Use: Distance ( feet) 300 Number of Pools I 57 Flow Level ( d): 0 Low rd~ oderate High Weather: 7k + lVL * wy Water Temperature: 6 O T-Water Clarity ( d): && ear Moderate Turbid FISH OBSERVATIONS AQUATIC WILDLlFE I , , , ' Species Sies Spedes Quantity If fish use ends, at a natural ba ' er, describe t e conditions that prevent upstream fish passage. The. LZ m c b r u f - ~ V~ L ry 54- p X e u e + he ed$+ t.* use. ~ k rlrcnu, RIIIVC ~ L I : : pain+ I S ~ 4 1 ~ g ~ r L ~ d eo5ve r bai( Lle r S, b+ + his ri- gf obnhi~ n o+ Q b r r r t c r. ' 7 If fish use ends at a road crossing, descn e conditions that may prevent upstream fish passage. U P Other comments ( use reverse side if necessary): N r 4.0r L r ~ s; Wj J bCqPn 5 u ru . + r + he L) wediunn - sws\ l size chaqc, F, sh U ~ CC ~ wJh c r t a d c c y t r ; b ~ + G~ d . ovt WLQ) ew- ker s LLII+. 26 FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Surveyor Name( s): 30 e Cadd i i , Bob hJvrnP1\ Agency: o ba~ ~ a'ndbwner: Lobsfec C r , ~ , , b c c Mailing Address: 7 D. ' 30K 2 , ~ J L pLet~ t , D R DO Phone: 8 YD- o 00 1 Date Surveyed: m4 I/ 2, i? 7- C I f Stream: / ) ~ ~ ~ ~ ek bS "" ~ c Tributaryto: L o b s t e r Lraek Quad Map: B V ' ~ Cr eek ??, d. ie Location: T 73 R 2 0 Sec. 3Y, ~ I. o AA. J G Survey Method ( d): d~ lectroshocker Angling 0 Visual Survey Above End of Fish Use: Distance ( feet) 2 5 0 Number of Pools / D Flow Level ( d): 0 Low d ~ o d e r a t e 0 High Weather: 94, & SU W\ I Water Temperature: 5- 7 " ?= Water Clarity ( d) : Wc1ea. r CI Moderate 0 Turbid FISH OBSERVATIONS AQUATIC WILDLIFE PHYSICAL STREAM DATA Species Sics Spedes If fish use ends at a natural barrier, describe the conditions that prevent upstream fish passage. Quantity If fish use ends at a road crossing, describe conditions that may prevent upstream fish passage. I I Other comments ( use reverse side if necessary): ~ h5ctre um WLS " r y ~ Lw iL tL ~ decy f- goo( r. @. la f is/., observe4 , Ty pr N ~ f . r e u ~ z . FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Surveyor Name( s): \ ce < . 3ab Tr cut Agency: u/ k2 Mailing ~ ddress: Z3R Rne St , b k n h( e dr ! OR ? d o 0 Phone: ZB?- 3333 Date Surveyed: stream: ~*- aweA Tributary to: c r & QuadMap: G l e w b ~ ~ e k Location: T \ 4 5 R 6 @ Sec. zS,, ~ 3t .+ S-Survey Method ( d): d~ lectroshocker Angling Visual Survey Above End of Fish Use: Distance ( feet) Number of Pools Q Flow Level ( d): 0 Low & oderate High Weather: C( ea c Water Temperature: 5?* F Water Clarity ( d): lW2ear 0 Moderate Turbid FISH OBSERVATIONS AQUATIC WILDLIFE Species Sizes Spedes Quantity PHYSICAL STREAM DATA If fish use ends at a natural barrier, describe the conditions that prevent upstream fish passage. U P If fish use ends at a road crossing, describe conditions that may prevent upstream fish passage. Title: Surveying forest streams for fish use Author: Oregon. Forest Practices Section; Oregon. Habitat Conservation Division Year: 1995, 2005, 2004 Oregon Department of Forestry Forest Practices Section 2600 State Street Salem, OR 97310 Dl Fish 8 Wildlife Oregon Department of Fish and Wildlife Habitat Conservation Division P. O. Box 59 Portland, OR 97207 Introduction Identifying Oregon streams that contain fish is an important part in carrying out the new Water Protection Rules. These rules aim to protect areas of benefi-cial uses, such as fish. First, however, the beneficial uses present in each forest stream must be correctly identified. At present, a large number of fish- bearing streams are not identified on stream classification maps. To correct this problem, the Oregon Department of Forestry ( ODF) and the Oregon Department of Fish and Wildlife ( ODFW) must complete comprehensive surveys to identify fish use on all non- federal forest streams in Oregon. This effort will require at least 3 to 5 years and a significant financial investment. Because many streams are not accurately classified, the new rules also tempo-rarily protect streams that are likely to contain fish. Under the rules, for example, if Stream A flows into a body of water known to contain fish, it is assumed that fish also are using Stream A, up to the point that a natural barrier blocks their way farther upstream ( see OAR 629- 57- 2100: ll( b) B). Once the survey efforts are complete, this interim rule will not be needed. Coordinated efforts by public agencies, landowners, and others to complete fish- presence surveys will assure that important fisheries resources are pro-tected in the most cost- effective way. Landowners or any interested party may collect stream- classification information so that the overall survey can be completed as quickly as possible. Many private forest landowners, in cooperation with Oregon Department of Fish and Wildlife, are now completing inventories of stream habitat conditions on their lands. In the future, these cooperative efforts may also include fish-presence surveys. This publication tells how to complete fish- presence surveys on forested streams. The guidelines cover: How to plan either " operation- specific" or " maximum upstream fish distribution" surveys The proper way to conduct surveys The proper time of year to conduct surveys Minimum efforts required in completing the surveys The legal requirements for completing the surveys How to provide information to Oregon Department of Forestry to update the stream classification maps The stream reclassification process Operation- specif ic surveys Maximum upstream distribution surveys Planning the survey There are two major types of survey: operation- specific surveys, and surveys to find the maximum upstream distribution of fish. Each type requires different planning and is conducted using different approaches. Operation- specific surveys are those to classify a stream only in the particular area of an operation. This kind of survey may not include efforts to determine the maximum upstream extent of fish use. An operation- specific survey takes minimal planning and coordination. However, it may be very inefficient in the long run because future activities in other areas of the stream may require additional surveys. An operation- specilk survey is very simple to complete. It starts at the down-stream end of the operation area and moves upstream either to the end of the operation area or to the end of fish distribution, whichever comes first. If the purpose of the survey is to prove no fish use, the surveyor must be sure to make at least the minimum effort required to find fish ( see the section on " Survey Effort" on page 10). This kind of survey is done on an entire stream reach or on multiple stream reaches rather than on a restricted portion of a stream. Often, all streams within a basin or reach are completely surveyed. In some cases, the surveys encompass entire ownerships or watersheds. The specific locations of planned operations are usually not the main factor in setting up this kind of survey but can help decide which areas to survey first. Surveys to find the maximum upstream extent of fish use may be the most efficient and cost- effective. Surveyors often cover a group of streams in one area at a time; therefore, travel time is minimized because, often, a group of streams can be easily reached by one common forest road. When travel time is less, the time spent actually completing surveys is greater. This kind of survey may require slightly more planning and coordination to assure efficiency and to minimize duplication of effort by adjacent landowners or by other public agencies, but overall this approach is more cost- effective than the operation-specific surveys. Surveying for the maximum upstream distribution of fish may take more plan-ning than an operation- specific survey, but it is still relatively simple. First, look at ODF Stream Classification Maps for the survey area to see the current extent of fish- use streams. Also note which streams are not classified at all. Next, decide where to start the survey. It may help your planning if you know the relationship between watershed basin area and fish use for your area. Contact the local ODFW office to find out whether these relationships have been established for streams in your area. The information predicts where fish use is " likely to end" and so will help you decide where to start your surveys. At this point, you also may want to consider operations that are planned for certain areas and decide to survey those areas first. After choosing a starting area, look at current road maps to find potential starting points for the survey ( see Figure 1). Look for access points ( such as road crossings) near the upper reaches of the stream. When possible, a survey should start near the highest accessible point in the watershed. If road access to the stream is limited, you may want to start the survey near the point at which the stream's classification size changes from " medium" to " small"; often this point is near the end of fish use ( see Figure 2, page 4). At the starting point, first sample upstream. If you find fish, continue the survey upstream until fish use ends. Be sure to continue sampling above the point at which fish use ends ( see " Survey Effort," page 10). If you make all the required efforts but do not find fish, then survey downstream from the original starting point until you find fish. When surveying downstream, it is important to walk on the streambank until you are ready to sample so that the water stays clear. Begin fish survey above road crossing Fish use extends at least this far Figure I . Selecting survey starting points in an area with a road crossing. Additional survey work may be required if the maximum distribution of fish seems to be affected by a road culvert. If the stream above the culvert has no fish, sample the pool immediately below the culvert. If you find fish in this pool or downstream near the culvert, the culvert is a possible barrier to fish passage. Describe the culvert and the stream on the survey form ( page 19). If you do not find fish in the pool below the culvert, continue the survey down-stream until you do see fish. Begin fish survey here \ \\ \ / I Fish use extends at least this far - - k I Figure 2. Selecting survey starting points, based on the stream- size classification, in an area without a road crossing. Surveys to find the maximum upstream distribution of fish may require sampling across several land ownerships. Be certain to get permission from other landowners before beginning the survey. Contacts with other landowners are also important to prevent a duplication of effort, because many landowners and agencies may be conducting fish- presence surveys. When figuring how many surveyors and how much time you'll need to com-plete surveys in your area, you may want to consider the Department of Forestry's experience. We found that sampling a township ( 36 square miles) required approximately 24 person- days in the Coast region, but an area the same size in the Blue Mountains required only 4 person- days. Survey methods The accuracy and reliability of survey results depend greatly on the methods used to conduct the survey. Methods range from simply looking in the stream ( visual observation) to more intensive and effective sampling with a backpack electroshocker. The method you choose depends on the availability of sam-pling equipment, the size of the stream, the flow and clarity of the water, and other factors. It is important to select a sampling method that is best for the type of survey and for the waters being sampled. If the sample method is not appropriate, the results of the survey will not be very useful. For example, just looking at a stream may tell you there are fish in it at that point, but it is not an acceptable way to find the maximum upstream extent of fish use. Surveys to show that fish are not present require more sampling and specialized equipment in order to provide reliable results. Whenever the survey uses methods other than an electroshocker, it's important to thoroughly explain on the survey report form the reasons for using the other methods. This is the simplest method; it involves only walking the stream to look for fish. It is best to wear polarized sunglasses to reduce glare from the water and to survey only when water conditions allow good visibility. It's also best to walk upstream so that you can " sneak up" on fish in pools. Fish often are near the upstream ends of pools waiting for food to drift toward them. Small fish, such as fry, often are in shallow water along the margin of the stream. Be very alert because fish usually will dart into cover when they detect any movement, especially in small headwater streams. It helps to toss bread crumbs, insects, small twigs, or bemes into the stream to entice the fish to leave cover. The visual method is best suited to small streams where pools aren't deep enough to prevent your seeing the fish. This method is also the least damaging to the fish because actual collection is not required. However, the value of survey results can be reduced by many factors such as cloudy water, surface glare on the water, overcast days ( reduced light), fish behavior, and even the surveyor's poor eyesight. For these reasons, this method is not effective for determining the maximum upstream limit of fish distribution, although it can be used to prove fish are in a certain reach of the stream. Snorkeling is a special method of visual observation that can work well in some situations. Snorkeling allows you to see underwater through a diving mask and breathing snorkel. This method can be used in larger waters where electroshockers are less successful, and it has been used to locate fry where other methods failed. Night snorkel surveys are particularly useful for observ-ing bull trout fry. Visual observation Hook and line Backpack electroshocker The hook- and- line method uses a rod and reel and relies on the feeding be-havior of the fish. In small streams, drop a baited hook into the deepest pools, where larger fish often are. Bait can include worms, single eggs, cheese, dry flies, or stream insects such as caddis larvae. Sample pools that have a lot of cover because those tend to support greater numbers of fish. As with the visual observation method, approach the pool cautiously to avoid alerting the fish. To minimize the risk of injuring or killing the fish, always use barbless hooks. The hook- and- line method can be used when conditions are not good for visual sampling; for example, when water is not clear, flow is high, or the day is overcast. This method may be the most effective for sampling some larger or deeper waters where visual and electroshocker methods can be ineffective. These waters include deep beaver ponds and large, steep streams where downstream barriers ( such as falls and very steep sections) keep fish out of the small tributaries. This method has limitations, though, depending on fish behavior and the life stage of the fish that are present. Fish may be reluctant to bite on cold days, or when the water is murky with sediment, or if the fish detect the surveyor's presence. Also, hook- and- line sampling is not effective if only fry are in the stream. This method also depends on the angling skills of the surveyor. As with the visual observation method, hook- and- line sampling may not be the best way to determine the maximum upstream distribution of fish in small streams, but often it can be used to find fish in larger waters. The most effective way to determine the upstream extent of fish is with a backpack electroshocker. Electroshocker sampling requires additional training and experience, though, to be effective and safe. A backpack electroshocker introduces an electric field into the stream that temporarily immobilizes fish. Stunned fish can be observed as they float in the water, or they can be captured in a small hand net for closer observation if necessary. As with other methods, it is best to work in an upstream direction, wear polarized glasses, and to approach the sampling site carefully to avoid alerting the fish. One person nets fish while another person operates the electroshocker. The netter should walk behind or beside the shocker to avoid alerting the fish. The electroshocker can be very effective for sampling in small streams even where brush or instream cover prevents most other sampling methods. In fact, an electroshocker is often most effective in areas with instream cover because fish usually concentrate in these locations. This method works in streams of various sizes but is less effective in larger streams and in deep pools, espe-cially large beaver ponds. Use electroshockers carefully to minimize killing fish. When properly adjusted and used, the electroshocker should stun the fish without killing them. The fish may escape if the current is set too low, but usually the surveyor will still see the fish and so be able to document fish presence. To sample effectively and minimize fish kill, set the electroshocker on the lowest practical voltage output and low- frequency currents ( low pulse rates). Before sampling, use a voltame-ter to test the electroshocker in a stream. If the voltameter is not available, it is a good idea to test the electroshocker in a stream that you know has fish before working in streams whose fish use you do not know. The test will tell you whether the equipment is working and the effects of using different settings. The surveyors' safety must be considered carefully before using this method. Electroshockers can injure or kill humans if not properly used. Surveyors should not use this method without proper training, including CPR training. Surveyors should work in crews of at least two. All surveyors should wear rubber waders and rubber gloves during stream shocking and never use dipnets with metallic handles; the nets should have wood or fiberglass handles. All members of an electroshocking crew should understand the proper operation procedures and potential dangers of this equipment. The effectiveness of electroshocker sampling depends on water conditions and on the skills of the electroshocker operator and the netter. The electroshocker method may not be so useful in high flows or in turbulent or murky water because the surveyors may not see immobilized fish. Another drawback to this method is that the electroshockers may not be widely available and can be expensive. However, with proper training and experience and under suitable survey conditions, this method is the best for accurately determining the maximum upstream extent of fish use. There may be situations where reliable results can be had by using methods not discussed here. For example, headwater beaver ponds may be effectively Other methods sampled by fishing for at least 48 hours with minnow traps baited with salmon eggs or commercial trout bait. Or, seine nets may be effective in beaver ponds or larger waters. If you are thinking about using these or other sampling methods, discuss it first with the departments of Fish and Wildlife and of Forestry. They will decide whether the proposed methods are appropriate and, if so, set the required minimum level of sample effort for the alternate method. A backpack electroshocker is the best way to get reliable information about the upstream extent of fish use or to prove a stream is m e N ( no fish use). Sur- Survey methods: vey data that document the presence of fish through other methods, such as a summary visual observation or hook- and- line, will always be used to classify streams as Type F as far up as the point of observation, even though the exact upstream extent of fish use may not be known. In some cases, methods other than an electroshocker may give reliable information about the maximum upstream distribution of fish. Examples include deep beaver ponds and large, steep streams in which barriers keep fish out of small upstream tributaries. In those cases, reliable results may be better obtained with hook- and- line sampling or with other methods. Whenever the survey is conducted by methods other than an electroshocker, the reasons for choosing the other method must be thor-oughly explained on the survey form. Timing the surveys Survey accuracy depends a lot on the time of year the survey is done and on stream conditions at that time. Since the purpose of the survey is to accurately document the presence or absence of fish, it is critical to do the survey when fish are expected to be using the upper reaches of a stream. This generally is near spawning times or soon after fry emerge, when stream flows are relatively high. A survey done during a low- flow period may not indicate the actual maximum upstream extent of fish use or accurately prove no fish use the stream. Fish may use the upper reaches of a stream for a limited time only, so fish- use surveys must be timed carefully. Surveys done at other than recommended times may not give a complete description of fish use. For example, if fish are found at other than the recommended survey times, the surveyed part of the stream can be classified as fish- bearing, but the maximum upstream extent of fish use may not be known. If fish are not found, that will not necessarily prove that the stream reach does not support fish use. Only if the survey is made at a time when fish are most likely to be there can the absence of fish be a reliable sign that no fish use that portion of the stream. Other factors can affect the reliability of the survey even if it is made at the proper time. Abnormal flows due to drought or extreme runoff could affect the distribution of fish or the sampling efficiency of the surveyor. So, it is best not only to do the sampling within the recommended time period but also when conditions are appropriate. In some cases, survey timing may not have much effect on the reliability of survey results. This could occur when factors other than seasonal flow patterns control the upstream extent of fish distribution. For example, streams that get most of their water from springs may not have seasonal flow variations, including summer flows low enough to control the upstream distribution of fish. Or, conditions other than low flow could be controlling distribution. For example, large, steep streams that have natural barriers such as falls and steep, impassable sections. In such cases, surveys taken outside the recommended time periods may yield reliable data. However, it is important to describe these conditions thoroughly on the survey forms to justify not following the recom-mended timing. See Table 1 for the recommended sampling periods for different regions of the state for normal water- flow years. Periods differ due to variations in stream flow patterns, fish species, and life- history traits of the species in the different areas. Contact the local ODFW office before sampling to find out the best time to survey the stream you are planning to sample. Table 1. General recommended time periods to sample streams, by geographic region, during nomull water- flow years. Please contact your local ODFW ofice before sampling in order to get specific timing recommendations for the stream you will be sampling. REGION of Recommended Georeaion Stream Survey Period WESTERNO REGON All Coast South Coast West Cascades Interior Siskiyou March 1 through May 3 1 EASTERONR EGON All except spring- fed April 1 East Cascades through June 30 Blue Mountains Spring- fed streams* Entire year * Spring- fed streams are streams that get most of their water Born groundwater sources and that have very minor seasonal variations in flow. Stream surveys must be done within certain time periods ( Table 1) if the purpose is to prove the stream does not contain fish or to document the maximum upstream extent of fish use. mming recommendations are based on normal water- flow years and may vary in some years. Contact the local ODFW office before sampling to get specific timing recommendations for the streams to be surveyed. Information gathered at other times of the year may be used to document fish presence but may not be reliable enough to establish upstream fish- use limits or to classify the stream as II) lpe N ( no fish use). Whenever the recommended survey timing is not used, it is important to explain the reasons on the survey form so that the data can be evaluated for reliability. ~ - ~ Survey timing: a summary Survey effort: a summary Survey effort The level of effort used to complete the survey also can affect the reliability of the survey results. If the level of effort or the amount of stream sampled is too little, it may be wrong to conclude that fish are not present. The following guidelines describe the minimum level of survey effort required to assure that the data are reliable. If the purpose of the survey is to show that no fish use the stream, the survey will be considered reliable only if it includes at least 50 yards of stream length md a minimum of six pools, each at least 1 foot deep, immediately upstream of the point at which the non- fish- bearing section begins. ( In some cases, the survey will have to cover much more than 50 yards of stream in order to also include the required six pools.) In addition, the survey must include sampling any beaver dam ponds in the upstream non- fish section. Surveyors are encouraged to exceed the minimum level of effort in order to be even more sure that fish are absent from a stream reach and that the maximum upstream extent of fish use has been found. A survey intended to show the absence of fish must sample at least 50 yards of stream distance and a minimum of six pools, each at least 1 foot deep, imme-diately upstream of the point at which fish use is believed to end. In addition, any beaver ponds upstream must be sampled as part of the survey. The require-ments for the methods used and the timing of the survey also must be met in order to document the absence of fish. Legal requirements In Oregon, the Department of Fish and Wildlife regulates the collection of fish for personal or scientific use. Generally, collection methods prohibited by the general angling regulations, such as electroshockers, traps, or nets, and collec-tions at times of the year when angling is closed will require a Scientific Collection Permit from the Oregon Department of Fish and Wildlife. Scientific Collection Permits can be issued to agencies, companies, or indi-viduals. Request an application from the Fish Division of the Oregon Depart-ment of Fish and Wildlife, P. O. Box 59, Portland, OR 97207; telephone ( 503) 229- 5410, extension 323. Submit the application at least 1 month before you plan to do the survey in order to be sure the permit can be issued in time. The application requests information about the collection method to be used, when and where collection will be made, and a summary of the proposed project. By law, surveyers must keep records of their collection activities and submit them to the Oregon Department of Fish and Wildlife. Surveys using the visual observation method ( including snorkeling) do not require any licenses or permits because fish are not physically collected. Sampling with the hook- and- line method during open fishing seasons requires only a valid angling license. However, Oregon resident landowners and their immediate families do not need angling licenses to fish on land they own and live on. In either case, the general ahgling regulations for the stream must be followed during hook- and- line sampling unless a Scientific Collection Permit is obtained. Additional restrictions on survey efforts may apply if the stream contains species that the state or federal government lists as sensitive, threatened, or endangered species. Please contact your local ODFW office to find out whether any of these species are likely to be in streams you plan to sample. Reporting survey results Give survey data to the local ODF district office so that district Stream Classi-fication Maps can be updated. On page 19 is a blank survey report form. It asks for information about the location of the stream; the methods, timing, and effort of the survey; the physical character of the stream; observations of fish and wildlife; and the presence of natural or human- created barriers to fish passage. complete one form for each stream reach where fish were ob-served or fish use was found to end. See Figure 3 ( page 12) for descriptions of some fish species common to $ mall, forested streams; these may help to identify fish seen during surveys. Detailed instructions for completing the survey form are on pages 14 through 18. Attach to the Fish Presence Survey Form a copy of the ODF Stream ClassM-cation Map for the surveyed area or, if that is not available, a copy of the 7.5 minute USGS topographic map for the area. Note the following information on the map. ( Examples of completed survey report forms and maps are on pages 21 through 30.) The area of the stream that was actually surveyed ( including the areas without fish) as part of the survey effort. Highlight in yellow the entire stream reach surveyed ( see examples on pages 25,28, and 30). The upper limit of fish use. Note this on the map by drawing a line across the stream and writing the letter F at that point. The name of the surveyor. The date the stream was surveyed. GENUS ONCORHYNCUS - PACIFIC SALMON IOENTIFICATION FEATURES OF JUVENILES Faint parr marks. extend little. if am: below latanl line. Lures SOCKEYE w GENUS ONCORHYNCUS- TROUT IDENTIFICATIOEI FUTURES OF JUVENILES pols in dorsal Teeth on of tongue Maxillary extend past rear margin on throat W - Of eye CUTTHROAT 5 - I 0 parr marks on ridge ahead of dorsal tongue astend & st rear mark on throat Y; V margin of eye STEELHEAD- RAINBOW Few or no spots i n tail Figure 3. Identification characteristics of some juvenile salmon and trout species that may be observed in forested streams. 3. Permission to enter private forest lands should be obtained from all land-owners before the surveys are conducted. 4. Fish- presence surveys should then be made according to the guidelines given in this publication. 5. The required survey information, recorded on the Fish Presence Survey Form and maps, should be given to the local ODF district office. 6. The ODF office will give copies of the completed survey forms and maps to the local office of the Oregon Department of Fish and Wildlife. 7. The Department of Forestry will review the information, usually in consul-tation with the Oregon Department of Fish and Wildlife, to determine whether the survey results are reliable. 8. Based on its assessment of data reliability, the Department of Forestry will make appropriate changes to the ODF Stream Classification Maps. 9. All affected landowners will be notified of the proposed stream classifica-tion changes, according to the notification rules ( OAR 629- 57- 2110( 2)). Instructions for completing the survey report form The following information should be reported on the Fish Presence Survey Form. These instructions are in the order that the information appears on the form. Complete one form for each stream reach or branch where fish were observed or fish use was found to end. This may require assigning codes to unnamed tributaries ( for example, " trib. a," " trib. b") so that survey data can be cross- referenced to the survey maps. Please refer to examples on pages 21 through 29. Surveyor Narne( s): The name of the person or persons responsible for con-ducting the survey and reporting the results. AgencyfCompany: The name of the agency or company that employs the surveyor ( if applicable). Landowner: The name of the landowner of the reach surveyed. Mailing Address and Phone: The address and phone number for the person responsible for the survey. Stream: The name of the stream as reported on the USGS or ODF Stream Classification Map for the area. If the stream is unnamed, report the stream as " unnamed" and list the tributary that it flows into (" Tributary to..."). Tributary to: The name of the main stream ( as reported on the USGS or ODF map) that the surveyed stream flows into. This is especially important if the surveyed stream is unnamed. Quad Map: The name of the USGS 7.5 minute topographic map that includes the reach of the stream surveyed. If the surveyed reach covers more than one quad map, report first the name of the map that shows the identified end- point of fish use and then give the other maps' names. Location: A legal description ( township, range, and section to at least the quarter section) of the location where fish use ends. Date Surveyed: The month, day, and year the fish survey was conducted. Survey Method: Check the box for the survey method used. If more than one method was used, check all that apply and note the most often used method in the comments section or in the form's margin. Survey Amount Above End of Fish Use: The length of stream reach that was surveyed immediately upstream of the identified end of fish use. Estimate ( in feet) the length surveyed, and give the number of pools sampled for fish in that section. A survey to prove the absence of fish must sample at least 50 yards of stream and at least six pools immediately upstream of the end of fish use. In addition, any upstream beaver ponds must also be sampled. Flow Level: The flow conditions at the time of the survey. Use the following categories of flow. Low: Ranges from a series of isolated pools to flowing across less than 75 percent of the average bankfull width. Moderate: Surface water is flowing across 75 to 90 percent of the average bankfull width. High: Surface water flowing across more than 90 percent of the average bankfull width. It is not recommended thatfih presence surveys be conducted at high jlows. Weather: The weather during most of the fish survey ( rainy, overcast, partly cloudy, sunny, snowy, etc.). Water Clarity: The water visibility during the survey. Use the following categories of water visibility. Clear: Visibility is good in pools, deep pools, and riffles. Moderate: Visibility is good only in riffles and shallow pools. Turbid: Visibility is poor in both riffles and pools. It is not recommended that fih presence surveys be conducted when water is turbid. Water Temperature ( optional): The temperature of the stream ( in degrees Farenheit) at the time of the survey. Fish observations Report the species and approximate size ranges of fish observed in the sur-veyed reach. Use Figure 3 ( page 12) as a guide to identifying some game fish species commonly found in small, forested streams. Use the following codes and instructions to complete this section. Species: Use the following names or codes to report fish observed during the survey. If you observe a species not listed here, such as Pacific lamprey, use its common name. Name Species Code Coho salmon Co Cutthroat trout Ct Rainbow troutfsteelhead Rb/ St Bull trout BUT Brook trout BT Unknown salmonid UnS Sizes: Report the size range of fish, in inches, by species. For example, the size range of coho observed could be reported as " 1- 4 inches." If you see several sizes of one species ( for example, some cutthroat trout in the " 1- to 2- inch range and others in the " 6- to 8- inch" range), list them separately. Aquatic wildlife The types of aquatic wildlife that may be observed include tailed frogs ( includ-ing juvenile " tadpoles"), Pacific giant salamanders, and Olympic salamanders. Species: Give the common name of the species, if known. If you don't know the species name, at least report observations by a general name such as " salamanders." Number: The number of aquatic wildlife in each species or group observed. Physical stream data Report the physical characteristics of the stream in the vicinity of the end- point of fish use. Report information separately for ( 1) the section immediately at and downstream of the end of fish use, and ( 2) the area upstream of the maximum extent of fish use. Following are specific instructions for collecting this information. Bankfull Channel Width: By eye, estimate the average width ( in feet) of the bankfull channel for the 100- foot sections above and below the end- point of fish use. The bankfull channel is the area that is scoured by water during average high flows. The edge of the bankfull channel can be identified by looking for changes in vegetation, in soils and litter characteristics, or in the shape of the bank. The bank often will abruptly change slope at the bankfull boundary. Vegetation at the boundary often changes from annual vegetation ( such as grasses) to more permanent vegetation such as trees and shrubs. Estimate the width across the channel between the edges of the bankfull level. Current Wetted Width: Visually estimate the average width ( in feet) of the channel that contains flow ( is wetted) at the time of the survey. Report the estimated averages for the 100- foot sections above and below the end of fish use. Channel Gradient: Measure the average stream gradient with a clinometer for the 100- foot sections above and below the end of fish use. me a piece of flagging at eye level on a branch or shrub, walk up or down the stream bank, and then use the clinometer to sight on the flagging while you are standing on the channel bottom. Read and report the percent gradient. ODF Stream Class Size: The stream size (" small," " medium," or " large") from the ODF Stream Classification Maps for the reaches immediately above and downstream of the end of fish use. Natural barriers This information is very important for understanding relationships between the presence of fish and the physical characteristics of the stream. Understanding these relationships can help determine where fish- presence surveys should be concentrated and help predict where fish are likely to occur if survey informa-tion is not yet available. Generally, natural barriers are permanent structures such as falls or vertical drops more than 8 to 10 feet high for salmon or steel-head or 4 feet high for trout. Log jams, drops over logs, beaver dams, or other organic structures generally are only temporary barriers to fish passage, but report them as well. If fish use ends at a natural barrier, such as a waterfall, bedrock chute or cascades, describe the conditions at the site. Include a description of: ( 1) the type of barrier, ( 2) the approximate height ( in feet), ( 3) the percentage of slope, ( 4) the length ( in feet) of the bedrock chute or cascades, and ( 5) any other conditions that may be limiting fish passage. If the potential barrier is a bedrock chute, note whether the bedrock contains pools or rough features ( such as rocks, boulders, or other breaks in the flow), or whether the water flows in an even, shallow pattern over the bedrock. Please note on the survey map the locations of any natural barriers encountered. If you encounter a natural barrier, also be sure to sample above this point because fish often are found above natural barriers. Road- crossing barriers This information also is very important for understanding relationships be-tween the presence of fish and the physical characteristics of the stream. Road-crossing barriers can alter the relationships. If fish use ends at a road- crossing barrier, such as a culvert, describe the conditions at the site. Describe the type of barrier and its measurements at the time of the survey such as ( 1) the diameter of the culvert, in inches, ( 2) the depth ( in inches) of water in the culvert, ( 3) the height ( in feet) of the jump ( drop) below the culvert or structure, ( 4) the depth ( in inches or feet) of the plunge pool below the culvert outfall, ( 5) the gradient or slope of the culvert, given as a percentage as read off a clinometer, ( 6) the length ( in feet) of the culvert, and ( 7) any other factors that could affect fish passage. Please note on the survey map the locations of any road- crossing barriers, even if they are not at the end- point of fish use. As with natural barriers, be sure also to sample above the site because fish often are found above road- crossing barriers. Other comments Any other comments or notations that you think may be pertinent to the fish survey. It helps to describe any notable habitat characteristics, for example " lots of instream wood," " very few pools in the reach," " heavy silt load in the stream." Use the reverse side of the form if necessary. FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Surveyor Name( s): Agency: Land Owner: Mailing Address: Phone: Date Surveyed: Stream: Tributary to: Quad Map: Location: T R Sec. Survey Method ( d): 0 Electroshocker 0 h & g 0 Visual Survey Above End of Fish Use: Distance ( feet) Number of Pools Flow Level ( d): 0 Low 17 Moderate High Weather: Water Temperature: Water Clarity ( d): Clear 17 Moderate 17 Turbid FISH OBSERVATIONS AQUATIC WILDLIFE PHYSICAL STREAM DATA If fish use ends at a natural barrier, describe the conditions that prevent upstream fish passage. If fish use ends at a road crossing, describe conditions that may prevent upstream fish passage. Other comments ( use reverse side if necessary): FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Surveyor Name( s): . be Sorveq , 3 Troo+, FI s h G n r u l l , I*? , S.; L. Agency: N/ C I Land Owner: k! 4~ 4f, l T; M ~ C C Mailing address:?.^. sox ~ g~,\ L L I M UF~ A \ ID~ R) jC? suo Phone: BSB- 5555 ate surveyed: A p ( ; i 2 8, ! ?? s I Stream: Un hawed , " Tr I b R!' Tributary to: lr3 F . 21 o k so- ~ r a& QuadMap: D\ A &\ dy Location: T 305 R 5 " L Sec. 30, sw/ sto Survey Method ( d): d~ lectroshocker Angling 0 Visual Survey Above End of Fish Use: Distance ( feet) I 86 ' Number of Pools Flow Level ( d): CI Low cd~ oderate High Weather: S owv Water Temperature: 7 O F I Water Clarity ( V): dclear Moderate I7 Turbid FISH OBSERVATIONS AQUATIC WILDLIFE Species I Snes 1 Spedes 1 Quant'ity 1 PHYSICAL STREAM DATA If fish use ends at a natural barrier, describe the conditions that prevent upstream fish passage. bk If fish use ends at a road crossing, describe conditions that may prevent upstream fish passage. prf+ Other comments ( use reverse side if necessary): f- 15 L wsz ewd 30 $& abov e f *; rd John50~ m ain\ ifi< ~ r o s s i n OH ~ f r e a ~ 7.% ~ 5t redw g d ~ e n f & ry s t u p abde + he a d 4' & sh use - p & f i a n 10%. 2 1 OREGON FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Fish & Wildlife Stream: ~) nr? euce, d " Tr t b, O " Tributary to: w F & n~ oq CC. Quad Map: old &\ A% Location: T 382 R 5E Sec.' 30, si/ Sw I Survey Method ( 4): ~ lectroshocker 0 Angling 0 Visual Survey Above End of Fish Use: Distance ( feet) 2 5' 0 Number of Pools 20 Flow Level ( d): 0 Low d ~ o d e r a t e High Weather: Lw+ Water Temperature: 6 0 F I Water Clarity ( d): dclear Cl Moderate Turbid FISH OBSERVATIONS AQUATIC WILDLIFE Species 1 Snes I! , Species Quantity If fish use ends at a natural bamer, desc ' be the conditions that prevent u stre m fish assage. Fid - 4s 4+ 2 S ' ~ r t i Lm* r? d\. A dJ @ cater also % 15& 5 ( ho& a. r. rp Q5 W F - buffis @ ere fouu\ d . opstr + ye If fish use ehs) at a roa d. crossmng, descnbe conhlons that may prevent upstream fish passage. Other comments ( use reverse side if necessary): w tfw+ were fbU 4 above % z 6 + of (~ la+ erf~ ll above fu 25fcof I sowe years. 22 fail s& i ro fish t@ f& probab/ y vp FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP stream: V A ~ ~ ~ + SC~" T & ~ ributaryto: u. F. 3ehbtja14 Creek Quad Map: old - b a t d ~ Location: T 3 S 5 R 5 E Sec. Survey Method ( d): d~ lectroshocker 0 Anghng 0 Visual Survey Above End of Fish Use: Distance ( feet) a 2 5 Number of Pools 2 Flow Level ( d): 0 Low & oderate 0 High Weather: SvMwv Water Temperature: I Water Clarity ( d): d l e a r 0 Moderate 0 Turbid FISH OBSERVATIONS AQUATIC WILDLIFE - ... . .: : :....: ' ' . . . . . . A , , , .: . . . . , . . , .&& : ! Species ... . ..$ pedes Quantity PHYSICAL STREAM DATA If fish use ends at a natural barrier, describe the conditions that prevent upstream fish passage. M/ A If fish use ends at a road crossing, describe conditions that may prevent upstream fish passage. FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Stream: West h r k Aobrson Cr eeG Tributary to: Johnrow Cre~ k Quad Map: ( ~ ( 4Ith .\ Ay Location: T 385 R 5 E Sec. 2?,, 5E/ sLJ I Survey Method ( d): dlectroshocker 0 Angling Visual Survey Above End of Fish Use: Distance ( feet) 3 00 Number of Pools t% Flow Level ( V): 0 Low d ~ o d e r ae t High Weather: j , y~ I Water Temperature: 60" F= Water Clarity ( d): & ear Moderate Turbid FISH OBSERVATIONS AQ- U ATIC WILDLIFE t Spedes Quantity 1 I PHYSICAL STREAM DATA + IH n D CtsL 5h-* If fish use ends at a natural barrier, describe the conditions that prevent upstream fish passage. N I A If fish use ends t a roqj crossiy, describ~ concl~~ tohnats may prevent upstr am fish passa e. ~ hrvctr ert a no? pQ59 ~ c - r b LOWOJQ 4 u. 4 9 ) drop at * rut-/&. b l d a r p fn qr p aI . 7, slop is 6 70 , and w ( onp 7 % fu~ lv er+ 1s ~ chul~ ledb e replace4 t bi s Svmncr. Other comments ( use reverse s~ de~ fn ecessa ): Lower ~ t r c a - q r d r r & a & e + LC cd en. Sf- rm* bb; M Ieok 30a4, but + k shaln. dry up ;* SOW years. FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Mailing Address: ?. c, 3 2 , AJLO ~ L4- T o R 70 00 Phone: b40 - oool Date Surveyed: / Ha v 2 / cj? T I stream: ~ nnclcr- ed , " 7- r; b k " Tributary to: Lobs k c Creek Quad Map: BULL Lrceu Rtdqc Location: T 35 R 2W S ~ C . ~ ~ N € + 4 Survey Method ( d): ~ lectroshocker Angling 0 Visual Survey Above End of Fish Use: Distance ( feet) 300 Number of Pools I 57 Flow Level ( d): 0 Low rd~ oderate High Weather: 7k + lVL * wy Water Temperature: 6 O T-Water Clarity ( d): && ear Moderate Turbid FISH OBSERVATIONS AQUATIC WILDLlFE I , , , ' Species Sies Spedes Quantity If fish use ends, at a natural ba ' er, describe t e conditions that prevent upstream fish passage. The. LZ m c b r u f - ~ V~ L ry 54- p X e u e + he ed$+ t.* use. ~ k rlrcnu, RIIIVC ~ L I : : pain+ I S ~ 4 1 ~ g ~ r L ~ d eo5ve r bai( Lle r S, b+ + his ri- gf obnhi~ n o+ Q b r r r t c r. ' 7 If fish use ends at a road crossing, descn e conditions that may prevent upstream fish passage. U P Other comments ( use reverse side if necessary): N r 4.0r L r ~ s; Wj J bCqPn 5 u ru . + r + he L) wediunn - sws\ l size chaqc, F, sh U ~ CC ~ wJh c r t a d c c y t r ; b ~ + G~ d . ovt WLQ) ew- ker s LLII+. 26 FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Surveyor Name( s): 30 e Cadd i i , Bob hJvrnP1\ Agency: o ba~ ~ a'ndbwner: Lobsfec C r , ~ , , b c c Mailing Address: 7 D. ' 30K 2 , ~ J L pLet~ t , D R DO Phone: 8 YD- o 00 1 Date Surveyed: m4 I/ 2, i? 7- C I f Stream: / ) ~ ~ ~ ~ ek bS "" ~ c Tributaryto: L o b s t e r Lraek Quad Map: B V ' ~ Cr eek ??, d. ie Location: T 73 R 2 0 Sec. 3Y, ~ I. o AA. J G Survey Method ( d): d~ lectroshocker Angling 0 Visual Survey Above End of Fish Use: Distance ( feet) 2 5 0 Number of Pools / D Flow Level ( d): 0 Low d ~ o d e r a t e 0 High Weather: 94, & SU W\ I Water Temperature: 5- 7 " ?= Water Clarity ( d) : Wc1ea. r CI Moderate 0 Turbid FISH OBSERVATIONS AQUATIC WILDLIFE PHYSICAL STREAM DATA Species Sics Spedes If fish use ends at a natural barrier, describe the conditions that prevent upstream fish passage. Quantity If fish use ends at a road crossing, describe conditions that may prevent upstream fish passage. I I Other comments ( use reverse side if necessary): ~ h5ctre um WLS " r y ~ Lw iL tL ~ decy f- goo( r. @. la f is/., observe4 , Ty pr N ~ f . r e u ~ z . FISH PRESENCE SURVEY FORM ATTACH A COPY OF THE 7.5 MINUTE ODF STREAM CLASS MAP Surveyor Name( s): \ ce < . 3ab Tr cut Agency: u/ k2 Mailing ~ ddress: Z3R Rne St , b k n h( e dr ! OR ? d o 0 Phone: ZB?- 3333 Date Surveyed: stream: ~*- aweA Tributary to: c r & QuadMap: G l e w b ~ ~ e k Location: T \ 4 5 R 6 @ Sec. zS,, ~ 3t .+ S-Survey Method ( d): d~ lectroshocker Angling Visual Survey Above End of Fish Use: Distance ( feet) Number of Pools Q Flow Level ( d): 0 Low & oderate High Weather: C( ea c Water Temperature: 5?* F Water Clarity ( d): lW2ear 0 Moderate Turbid FISH OBSERVATIONS AQUATIC WILDLIFE Species Sizes Spedes Quantity PHYSICAL STREAM DATA If fish use ends at a natural barrier, describe the conditions that prevent upstream fish passage. U P If fish use ends at a road crossing, describe conditions that may prevent upstream fish passage. Close

• 11. [Image] Programmatic environmental assessment for Klamath Basin Ecosystem Restoration Office Projects, 2000-2010

  	Programmatic Environmental Assessment Summary This Environmental Assessment (EA) provides compliance with the National Environmental Policy Act (NEPA) for restoration actions undertaken by the US Fish ...
  	Citation × Citation Citation Abstract Copy Title: Programmatic environmental assessment for Klamath Basin Ecosystem Restoration Office Projects, 2000-2010 Author: U.S. Fish and Wildlife Service. Klamath Basin Ecosystem Restoration Office. Year: 2000, 2005, 2004 Programmatic Environmental Assessment Summary This Environmental Assessment (EA) provides compliance with the National Environmental Policy Act (NEPA) for restoration actions undertaken by the US Fish & Wildlife Service's Klamath Basin Ecosystem Restoration Office (ERO) in Klamath Falls, Oregon. These restoration activities are needed due to the large-scale loss of wetland and riparian habitat and degraded water quality. The purpose of these restoration efforts is the improvement of conditions of the watershed with specific regard to habitat and water quality, resulting in, among other benefits, improved conditions for the endangered fish species (bull trout and Lost River and shortnose sucker) populations of the basin. The geographic scope of this EA is defined as the upper Klamath River basin, including the entire watershed from Irongate Dam upstream to the headwaters. This EA is intended to provide NEPA compliance for restoration projects conducted between the years 2000 and 2010. The ERO was established in 1993 to sponsor and assist with a variety of restoration activities in the Klamath Basin. The ERO funds and provides technical assistance to restoration projects involving private landholders, concerned groups, and other state, federal, and tribal agencies. Four alternatives are presented in this EA. The proposed alternative (Alternative 1) consists of a comprehensive program of ecosystem restoration, promoting projects in both riparian areas and in upland habitats. This would continue the current program in effect since 1994. NEPA compliance would primarily be carried out via a single, programmatic document saving time and funds. The Fish & Wildlife Service proposes to fund and administer the following projects types: Riparian Projects: (fencing for livestock management; native plant establishment & diversification; non-native plant removal/control; erosion control; contour re-establishment; impoundment removal; wildlife habitat improvements) Wetland Projects: (fencing; wetland restoration and enhancement; wildlife habitat improvements) Upland or Road Projects: (road abandonment, decommissioning, & obliteration; road drainage improvements and storm proofing, re-establishment of historic contours; silvicultural treatments; native plant establishment/diversification; non-native plant removal/control; fencing; landslide treatments; culvert/stream crossing upgrades; erosion control; wildlife habitat improvements). In-stream Projects: (habitat complexity and diversity improvements; hydrologic regime improvements; coarse woody debris supplementation; natural or artificial barrier removal, modification &/or creation; fish screens installation). Alternative 2 would concentrate restoration efforts only on riparian, instream, and wetland areas. Road projects would be conducted only within the riparian corridor, as defined. NEPA compliance would also be conducted programmatically. Alternative 3 would cease all restoration activities conducted and funded by the ERO in the Klamath Basin. This alternative would serve as a benchmark against which the effects of the restoration alternatives discussed above can be compared. Alternative 4, the "No Action" alternative, would continue current management policies with regard to NEPA compliance, providing compliance on a project by project basis requiring independent analysis for each project. The affected environment of the region is described in detail. The environment has been changed significantly since the 1890's due to logging, agriculture and urban development. An extensive system of dams, canals, and drainage structures has resulted in the conversion of approximately 80% of pre-settlement wetlands to agricultural uses. Riparian corridors have been similarly impacted, and upland forests regions have been affected by logging, road construction and other factors. These changes have contributed to problems with the water quality in the region, contributing to the listing of several fish species as threatened or endangered; loss of habitat has affected a large number of other species as well. The environmental effects of each alternative is analyzed. Some short term negative impacts could occur as a result of the projects authorized by both Alternative 1 and Alternative 2, but these would be strongly offset by the expected beneficial results to water quality and habitat conditions. Alternative 1 would be expected to have a greater overall effect on the environment than Alternative 2, since many of the underlying factors with which restoration efforts are concerned originate in upland conditions (i.e. sedimentation and hydrologic functionality). Alternative 3 would result in conditions remaining much as they are currently, although other programs and organizations are making efforts at restoration activities. The environmental impacts of individual projects anticipated under Alternative 4 would be generally the same as for similar projects under Alternative 1. The primary difference between the two alternatives would be the higher efficiency and improved cumulative analysis resulting from a programmatic approach as proposed in Alternative 1. Public participation in the NEPA process has been, and will continue to be, solicited and welcomed. Compliance with state and federal laws and regulations such as the Clean Water Act, National Historic Preservation Act, and the Endangered Species Act, as well as guidelines for contaminant surveys, will be carried out as detailed. While these projects are expected to play an important role in the restoration of the region, none of these alternatives are expected to have a significant impact when compared with the loss of wetland, riparian and upland habitats over the past century, impacts which do occur would be of a cumulatively beneficial nature. Other restoration efforts are being carried out in the area by other governmental and private groups, and it is expected that these combined efforts will achieve important beneficial results for the ecosystem. Title: Programmatic environmental assessment for Klamath Basin Ecosystem Restoration Office Projects, 2000-2010 Author: U.S. Fish and Wildlife Service. Klamath Basin Ecosystem Restoration Office. Year: 2000, 2005, 2004 Programmatic Environmental Assessment Summary This Environmental Assessment (EA) provides compliance with the National Environmental Policy Act (NEPA) for restoration actions undertaken by the US Fish & Wildlife Service's Klamath Basin Ecosystem Restoration Office (ERO) in Klamath Falls, Oregon. These restoration activities are needed due to the large-scale loss of wetland and riparian habitat and degraded water quality. The purpose of these restoration efforts is the improvement of conditions of the watershed with specific regard to habitat and water quality, resulting in, among other benefits, improved conditions for the endangered fish species (bull trout and Lost River and shortnose sucker) populations of the basin. The geographic scope of this EA is defined as the upper Klamath River basin, including the entire watershed from Irongate Dam upstream to the headwaters. This EA is intended to provide NEPA compliance for restoration projects conducted between the years 2000 and 2010. The ERO was established in 1993 to sponsor and assist with a variety of restoration activities in the Klamath Basin. The ERO funds and provides technical assistance to restoration projects involving private landholders, concerned groups, and other state, federal, and tribal agencies. Four alternatives are presented in this EA. The proposed alternative (Alternative 1) consists of a comprehensive program of ecosystem restoration, promoting projects in both riparian areas and in upland habitats. This would continue the current program in effect since 1994. NEPA compliance would primarily be carried out via a single, programmatic document saving time and funds. The Fish & Wildlife Service proposes to fund and administer the following projects types: Riparian Projects: (fencing for livestock management; native plant establishment & diversification; non-native plant removal/control; erosion control; contour re-establishment; impoundment removal; wildlife habitat improvements) Wetland Projects: (fencing; wetland restoration and enhancement; wildlife habitat improvements) Upland or Road Projects: (road abandonment, decommissioning, & obliteration; road drainage improvements and storm proofing, re-establishment of historic contours; silvicultural treatments; native plant establishment/diversification; non-native plant removal/control; fencing; landslide treatments; culvert/stream crossing upgrades; erosion control; wildlife habitat improvements). In-stream Projects: (habitat complexity and diversity improvements; hydrologic regime improvements; coarse woody debris supplementation; natural or artificial barrier removal, modification &/or creation; fish screens installation). Alternative 2 would concentrate restoration efforts only on riparian, instream, and wetland areas. Road projects would be conducted only within the riparian corridor, as defined. NEPA compliance would also be conducted programmatically. Alternative 3 would cease all restoration activities conducted and funded by the ERO in the Klamath Basin. This alternative would serve as a benchmark against which the effects of the restoration alternatives discussed above can be compared. Alternative 4, the "No Action" alternative, would continue current management policies with regard to NEPA compliance, providing compliance on a project by project basis requiring independent analysis for each project. The affected environment of the region is described in detail. The environment has been changed significantly since the 1890's due to logging, agriculture and urban development. An extensive system of dams, canals, and drainage structures has resulted in the conversion of approximately 80% of pre-settlement wetlands to agricultural uses. Riparian corridors have been similarly impacted, and upland forests regions have been affected by logging, road construction and other factors. These changes have contributed to problems with the water quality in the region, contributing to the listing of several fish species as threatened or endangered; loss of habitat has affected a large number of other species as well. The environmental effects of each alternative is analyzed. Some short term negative impacts could occur as a result of the projects authorized by both Alternative 1 and Alternative 2, but these would be strongly offset by the expected beneficial results to water quality and habitat conditions. Alternative 1 would be expected to have a greater overall effect on the environment than Alternative 2, since many of the underlying factors with which restoration efforts are concerned originate in upland conditions (i.e. sedimentation and hydrologic functionality). Alternative 3 would result in conditions remaining much as they are currently, although other programs and organizations are making efforts at restoration activities. The environmental impacts of individual projects anticipated under Alternative 4 would be generally the same as for similar projects under Alternative 1. The primary difference between the two alternatives would be the higher efficiency and improved cumulative analysis resulting from a programmatic approach as proposed in Alternative 1. Public participation in the NEPA process has been, and will continue to be, solicited and welcomed. Compliance with state and federal laws and regulations such as the Clean Water Act, National Historic Preservation Act, and the Endangered Species Act, as well as guidelines for contaminant surveys, will be carried out as detailed. While these projects are expected to play an important role in the restoration of the region, none of these alternatives are expected to have a significant impact when compared with the loss of wetland, riparian and upland habitats over the past century, impacts which do occur would be of a cumulatively beneficial nature. Other restoration efforts are being carried out in the area by other governmental and private groups, and it is expected that these combined efforts will achieve important beneficial results for the ecosystem. Close

• 12. [Image] Crisis to consensus : restoration planning for the Upper Klamath Basin

  	Executive Summary This report presents the Upper Klamath Basin Working Group's (Working Group) recommendations for the development and implementation of a restoration plan for the Upper Klamath Basin. ...
  	Citation × Citation Citation Abstract Copy Title: Crisis to consensus : restoration planning for the Upper Klamath Basin Author: Upper Klamath Basin Working Group Year: 2002, 2005, 2004 Executive Summary This report presents the Upper Klamath Basin Working Group's (Working Group) recommendations for the development and implementation of a restoration plan for the Upper Klamath Basin. In 1996, the 104th Congress of the United States chartered the Upper Klamath Basin Working Group (Public Law 104-333 - the Oregon Resources Conservation Act) to develop a plan for the Upper Basin that focuses on enhancing ecosystem restoration, improving economic stability, and minimizing impacts associated with drought on all resources and stakeholders. The Working Group is comprised of over 30 individuals appointed by the Governor of Oregon, representing federal, state, and local governments and agencies; the Klamath Tribes; conservation organizations; farmers and ranchers; and industry and local businesses. The objective of the Working Group is to develop and oversee a restorative course of action that allows for mutually beneficial gains for stakeholders wherein everybody in the Upper Basin can achieve positive, affirming results together, and where no one is left economically, culturally, or spiritually disadvantaged. Chapter 1 of this report presents a brief summary of the history of the Working Group and the conditions leading to the development of this effort. Chapter 2 describes the facilitated "interim planning process" the Working Group engaged in between April 2001 and July 2002. Chapter 3 presents the results of the interim planning process including key recommendations regarding Working Group decision-making and operating rules, technical data needs, future cost and time frame of the restoration planning process, and similar planning decisions. Chapter 4 describes the next steps and actions the Working Group is prepared to take to lead the restoration planning process. The Working Group's goals and objectives will be achieved through the Working Group's continued commitment to public outreach, collaborative problem solving, and implementation of real world solutions. Desired outcomes from implementation of the restoration plan include, but are not limited to, the following: improved water quality through the implementation of accepted Best Management Practices; restoration of wetlands and riparian habitat; enhancement of natural and structural water storage; improvements to irrigation efficiency and water conservation; economic growth and diversity through activities such as value added natural resource products and ecotourism; and enhancement of wildlife Tribal Trust resources. Title: Crisis to consensus : restoration planning for the Upper Klamath Basin Author: Upper Klamath Basin Working Group Year: 2002, 2005, 2004 Executive Summary This report presents the Upper Klamath Basin Working Group's (Working Group) recommendations for the development and implementation of a restoration plan for the Upper Klamath Basin. In 1996, the 104th Congress of the United States chartered the Upper Klamath Basin Working Group (Public Law 104-333 - the Oregon Resources Conservation Act) to develop a plan for the Upper Basin that focuses on enhancing ecosystem restoration, improving economic stability, and minimizing impacts associated with drought on all resources and stakeholders. The Working Group is comprised of over 30 individuals appointed by the Governor of Oregon, representing federal, state, and local governments and agencies; the Klamath Tribes; conservation organizations; farmers and ranchers; and industry and local businesses. The objective of the Working Group is to develop and oversee a restorative course of action that allows for mutually beneficial gains for stakeholders wherein everybody in the Upper Basin can achieve positive, affirming results together, and where no one is left economically, culturally, or spiritually disadvantaged. Chapter 1 of this report presents a brief summary of the history of the Working Group and the conditions leading to the development of this effort. Chapter 2 describes the facilitated "interim planning process" the Working Group engaged in between April 2001 and July 2002. Chapter 3 presents the results of the interim planning process including key recommendations regarding Working Group decision-making and operating rules, technical data needs, future cost and time frame of the restoration planning process, and similar planning decisions. Chapter 4 describes the next steps and actions the Working Group is prepared to take to lead the restoration planning process. The Working Group's goals and objectives will be achieved through the Working Group's continued commitment to public outreach, collaborative problem solving, and implementation of real world solutions. Desired outcomes from implementation of the restoration plan include, but are not limited to, the following: improved water quality through the implementation of accepted Best Management Practices; restoration of wetlands and riparian habitat; enhancement of natural and structural water storage; improvements to irrigation efficiency and water conservation; economic growth and diversity through activities such as value added natural resource products and ecotourism; and enhancement of wildlife Tribal Trust resources. Close

• 13. [Image] An examination of the Klamath Basin crisis : restructuring the discourse within an identity-based framework

  	Thesis (B.A.) -- Whitman College, 2002; Includes bibliographical references (leaves 79-83)
  	Citation × Citation Citation Abstract Copy Title: An examination of the Klamath Basin crisis : restructuring the discourse within an identity-based framework Author: Dornsife, Alison M. Year: 2002, 2005, 2004 Thesis (B.A.) -- Whitman College, 2002; Includes bibliographical references (leaves 79-83) Title: An examination of the Klamath Basin crisis : restructuring the discourse within an identity-based framework Author: Dornsife, Alison M. Year: 2002, 2005, 2004 Thesis (B.A.) -- Whitman College, 2002; Includes bibliographical references (leaves 79-83) Close

• 14. [Image] The Klamath Basin sucker species complex

  	One chapter of a seven chapter annual report from 1999 examining ecological issues regarding the shortnose and Lost River sucker populations in Upper Klamath Lake and Williamson River.
  	Citation × Citation Citation Abstract Copy Title: The Klamath Basin sucker species complex Author: Oregon Cooperative Wildlife Research Unit Year: 2000, 2005 One chapter of a seven chapter annual report from 1999 examining ecological issues regarding the shortnose and Lost River sucker populations in Upper Klamath Lake and Williamson River. Title: The Klamath Basin sucker species complex Author: Oregon Cooperative Wildlife Research Unit Year: 2000, 2005 One chapter of a seven chapter annual report from 1999 examining ecological issues regarding the shortnose and Lost River sucker populations in Upper Klamath Lake and Williamson River. Close

• 15. [Image] Molecular evolution and ecology of Klamath Basin suckers. Part B - Evidence for a lethal homozyhous genotpe at the Ankyrin(g) locus in Klamath Basin suckers (Catostomidae)

  	One chapter of a seven chapter annual report from 1999 examining ecological issues regarding the shortnose and Lost River sucker populations in Upper Klamath Lake and Williamson River.
  	Citation × Citation Citation Abstract Copy Title: Molecular evolution and ecology of Klamath Basin suckers. Part B - Evidence for a lethal homozyhous genotpe at the Ankyrin(g) locus in Klamath Basin suckers (Catostomidae) Author: Oregon Cooperative Wildlife Research Unit Year: 2000, 2005 One chapter of a seven chapter annual report from 1999 examining ecological issues regarding the shortnose and Lost River sucker populations in Upper Klamath Lake and Williamson River. Title: Molecular evolution and ecology of Klamath Basin suckers. Part B - Evidence for a lethal homozyhous genotpe at the Ankyrin(g) locus in Klamath Basin suckers (Catostomidae) Author: Oregon Cooperative Wildlife Research Unit Year: 2000, 2005 One chapter of a seven chapter annual report from 1999 examining ecological issues regarding the shortnose and Lost River sucker populations in Upper Klamath Lake and Williamson River. Close

• 16. [Image] Effects of water quality on growth of juvenile shortnose suckers, Chasmistes brevirostris (Catostomidae: Cypriniformes), from Upper Klamath Lake, Oregon

  	One chapter of a seven chapter annual report from 1999 examining ecological issues regarding the shortnose and Lost River sucker populations in Upper Klamath Lake and Williamson River.
  	Citation × Citation Citation Abstract Copy Title: Effects of water quality on growth of juvenile shortnose suckers, Chasmistes brevirostris (Catostomidae: Cypriniformes), from Upper Klamath Lake, Oregon Author: Oregon Cooperative Wildlife Research Unit Year: 2000, 2005 One chapter of a seven chapter annual report from 1999 examining ecological issues regarding the shortnose and Lost River sucker populations in Upper Klamath Lake and Williamson River. Title: Effects of water quality on growth of juvenile shortnose suckers, Chasmistes brevirostris (Catostomidae: Cypriniformes), from Upper Klamath Lake, Oregon Author: Oregon Cooperative Wildlife Research Unit Year: 2000, 2005 One chapter of a seven chapter annual report from 1999 examining ecological issues regarding the shortnose and Lost River sucker populations in Upper Klamath Lake and Williamson River. Close

• 17. [Image] Public notice opening public lands to entry and announcing availability of water therefor : Public notice no. 45, October 8, 1947, Klamath Project Oregon-California, Part 2 - Tule Lake Division

  	UNITED STATES DEPAXTMENT OF. THE INTERIOR BUREAU OF RECLAMATION Washington, D. C. Public Notice No. I45 October 8, 1947 KLAMATH PROJECT, OREMN - CALIFORNIA PAXT 2- TLILE LAKE DIVISION PUBLIC NOTICE ...
  	Citation × Citation Citation Abstract Copy Title: Public notice opening public lands to entry and announcing availability of water therefor : Public notice no. 45, October 8, 1947, Klamath Project Oregon-California, Part 2 - Tule Lake Division Author: United States. Bureau of Reclamation Year: 1947, 2005, 2004 UNITED STATES DEPAXTMENT OF. THE INTERIOR BUREAU OF RECLAMATION Washington, D. C. Public Notice No. I45 October 8, 1947 KLAMATH PROJECT, OREMN - CALIFORNIA PAXT 2- TLILE LAKE DIVISION PUBLIC NOTICE OPENING PUBLIC LANDS TO ENTRY AND ANNOUNCING AVAILABILITY OF WATER THRWOR 1. Public land for vhich water i s available and for + ich entry may be made.-- In pursuance of the Act of June 17, 1902 ( 32 Stat. 388) and acts amendatory thereof or supplementary thereto, it i s hereby announced that water w i l l be available beginning with the i r r i ~ a t i o ns eason of 1948, end thereafter, and that application may be made in accordance with t h i s notice, beeinnine a t 2: 00 p. m., October 22, 1947, for entry on public lands i n Part 2- file Lake Division of the KlamAth Project,, Oregon - California, as shown on approved farm unit plats on f i l e in the Office of the District Manaaer. Bureau of Reclamation. Klamath Falls. Oregon. and in the District Land Office a t Sacramento, ~ a l i r o r k a . These lands are dkcribed as fofiows:- . Mount Diablo Meridian. California Section 1 36 1 1 1 1 1 1 1 2 1 2 2 2 3 2 3 2 2 2 1 11 12 1 11 11 - Farm - Unit A B C D E F G H J A B C D E F K L A B Description Township 46 North. Ranp( e 5 % st Lots 1, 8 & ~"$ IE& ( T. C7 N., R. 5 E.) Lo* 10 Lots 2, 7 & 9 i ~ t ~ & Lots 3, 6 & SEN& Lots 12 and 15 Lot 18 ~ 4 SWk ~ 4 % E& E& Lots 4 & 5 Lots 13 & 14 ~ o1t & NNE~ Lot 2 & SE& NW~ Lot 3 Lot 20 swl. Srwt Lot 22 E!& '& a h t s 6 & 7 Lots 16 & 17 Lots 4 & 5 Lot 6 Lot 19 ww4 @ NWt Total Irri-gable Acres 86.7 81.9 84.6 84.2 72.9 73.8 71.4 72.0 n. 4 73.5 73.4 84.0 86.6 * 77.3 75.5' n. 8 68.8 75.2 Order of Selection Section 11 u 11 ll 12 12 12 12 12 12 12 12 12 35 35 34 35 34 35 35 36 36 6 6 7 6 7 7 7 - Farm - Unit C D E J A B C D E F G H A B C D i3 B C A B C A B D Total Irri- Description gable Acres Township 46 North. Rawe 5 East( contd. 1 L c t s 6 & 7 Lots 7 & 8 Lot 9 Township 427eh. Range 5 East Lots 12 & 13 Lots 11 & 14 Lot 9 $ 94 Lot 10 Lot 3 w& i Lots 4, 8 & 9 Township 46 North. Range 6 East Lcts 15, 16 & 18 Lots 6, 10, 17, 20 & 21 Lots 15, 16, Lots 22 & 23 Lots 7, 11, 17, 18, SZ$ NI+~ Lots 8, 12 & NE$ SW& Lots 9, U & sE$& Order of - Sslection 2. & nit of acreaKe for which entry may be made or water secured.-? he area of public land constituting each farm unit represents the acreage which, in the opinion of the Secretary of the Interior, may be reasonably reouired for the support of a family upon such land, and i s fixed a t the amount shown upon the farm unit plats referrcd to above. 3. Preference rinhts of veterans. Nature of reference.-- Pursuant to the provisions of the A- ct of September 27, 1944 ( 58 Stat. ai47>- dyt?;;; Acts of June 25, 1946 ( Public Law 440, 79th Congress, 2nd ~ e s s i o n ) , and May 31, 1947 ( Public Law 82, 80th Congress, 1st session), for a period of 90 days from the opening of these lands to entry, or u n t i l January 20, 1948, the lands described i n paragraph 1 above w i l l be opened t o entry to persons who a t the time of milking application f a l l within one of the following classes: ( 1) Persons, including persons under 21 years of age, who have served i n the Army, Navy, Marine Corps, or Coast Guard of the United States for a period of a t l e a s t 90 days a t any time on o r a f t e r September 16, 1940, and prior to the termination of the present war, and are honorably discharged therefrom. ( 2) Persons, including persons under 21 years of age, who have served i n said Amy, Nairy, Marine Corps or Coast Guard during such period, regardless of l e n ~ t ho f service, and are discharged on account of wounds received or disability incurred during such period i n the line of duty, or, subsequent t o a regular discharge, are furnished hospitalization or awarded compensation by the government on account of such wounds or disability. ( 3) Ihe spouse of any person i n e i t h e r of the above classes ( 1) and ( 2), provided such spouse has the consent of such person to exercise his o r her preference right under said Act. ( L) The surviving spouse of any person i n either of the above classes ( 1) and ( 2), or i n the case of the death or marriage of such spouse, the minor child or children of such person by a guardian duly appointed and o f f i c i a l l y accredited a t the Department of the Interior, ( 5) The surviving spouse of m p person whose death has resulted from wunds received or disability incurred i n l i n e of duty while s e r v i n ~ i n said Army, Navy, Marine Corps or Coast , Tuard during the aboveaentioned period, or i n the case of the death or mrriage of such spouse, the oinor child or children of such person by a guardian duly appointed and o f f i c i a l l y accreEited a t tile Department of the Interior. Provided, however, that persons claiming such preferences must be qualified t o make entry under the homestead laws and also possess the qualifications as t o industw, experience, character, capital, and physical fitness required of a l l entrymen and entrywomen under t h i s notice. b. Definition of honorable discharge.- An honorable discharge within the meaning of the Act of Septenber 27, 1964, as amended, shall mean: ( 1) Separation of the veteran from the service by means of an honorable discharge or a discharge under honorable conditions. ( 2) Transfer of the veteran with honorable service from such service to a reserve or r e t i r e d s t a t u s prior to the termination of the war, or ( 3) Ending of the period of such veteran's war service by reason of the temination of the war, even though the veteran remains i n the military or naval service of the United States. c. Submission of proof of veterans' status.- All applicants for farm units who claim veterans* preference must attach to t h e i r applications a photostatic, c e r t i f i e d , or authenticated copy of an o f f i c i a l document of the respective branch of the service involved which clearly indicates an honorable discharge or transfer to a reserve o r retired status or which constitutes eddence of other facts on which the claim for preference i's based. Where the preference i s claimed by the surviving spouse, or on behalf of the minor child or children, of a deceased veteran, proof of such relationship, of his military service, and of his death must be attached to the application. Where the preference i s claimed by the spouse of a livinz veteran, proof of such relationship, the written consent of such veteran, and proof of his military service as re, mired above must be attached to the application. 4. Qualifications required by the Reclamation Law.-- Pursuant to the provisions of subsection C, section I+. of the Act of December 5. 1924 ( L3 Stat. 702. 43 U. S. C. 433). the follow in^ are established as minimrun nualifications which, in'the opinion of the iocal examjning koe. rd, are necessary to insure the success of entrymen or entrywomen on reclamation farm units included under t h i s notice. Appli-cants must meet these qualifications, as determined by the exanAninc boerd, i n order to he considered for entry. Failure to meet them i n any single respect will be sufficient cause for rejection of an application. No credit wi'll be given : or qualifications i n excess of the minimum reouired. The minimum qualifications are as follows: l a. Character and industry.- The applicant must be possessed of honesty, temperate habits, t h r i f t , industry, seriousness of purpose, record of good moral conduct, an8 a bona f i d e i n t e n t t o engage in farming as an occupation. As part of each application, the applicant shall furnlsh three separate signed statements regarding the character and industry of the applicant. These statements may be prepared and signed by an ordained sinister, any commanding officer under whom the applicant served, a teacher or administrative o f f i c i a l of any recognized high school o r college, present or previous employer or any comparable individual or o f f i c i a l , not a relative, who i s personally acquainted with the applicant. The individuals signing these statements may be those l i s t e d in para-graph 17 of the farm application blank, referred to i n paragraph 6 of t h i s notice. \ b. Health.-- The applicant must be i n such physical condition as w i l l enable him t o engage i n n o m l farm labor. Any person who i s physically handicapped or afflicted with any condition which makes such a b i l i t y questionable must attach to his application the detailed statement of an examining physician which defines the limitation upon such a b i l i t y and i t s causes. c. Farm experienn. ( 1) Fam experience shall be of such a n a t ~ r ea s in the judgment of the examining board w i l l qualify the applicant to undertake the development and operation of an irrigated farm by modern methods. The applicmt must have had a minimum of twa years' full- time farm experience a f t e r attain-ing the age of 15 years. ' Iko years of study i n agricultural courses i n an accredited agricultural college or tw years of responsible technical work in agriculture, i f deemed by the examining board to be work which would contlribute toward successful farm operation, may be substituted for one year of full- time experience; pmvided that no more thnn one year's experience may be credited from such sources. . A farm youth having atteined the age of 15, who actually resided and wrked on a farm h i l e attending school, majr credit such part- time experience as equal to 50 percent of full- time experience. A l l fam experience must have been obtained since October 1, 1932. No advantage w i l l accrue from farming ex-perienae on irrigated land. ( 2) Applicants must furnish three separate statements each signed either by a Vocational Agricultural teacher, County Agent, Farmers Home Administration County Supervisor, A. A. A. County Chairman, an officer of any local farm organization, or by some other responsible person who has personal knowled~ e of the applicant's farm experience or has verified it to h i s satisfaction certifying t o the farm experience claimed i n paragraph 7 of the farm application blank. Forms to be used by these references accompany each farm application blank. ( 3) Women applicants must describe fully the farm a c t i v i t i e s i n which they have participated and the relation of any agricultural courses they have taken to farm operation and management. d. Capital.-- Each applicant must possess at least $ 2,000, consisting of cash or assets readily convertible into cash, such as United jtates Savings Bonds, or assets useful i n the operation of a fann, such as livestock, farm machinery and equipent. In addition, each applicant shall furnish, i n the space pmvided i n paragraph 11 of the farm application blank, a financial statement l i s t i n g all of h i s assets and all of h i s l i a b i l i t i e s , showing a net worth of a t l e a s t 92,000. " Possession of the minimum net Worth rewrement of at least $ 2,000 must be corroborated hy a statement of an o f f i c i a l of a bank, or other responsible and reputable private or public credit agency. This corroborative statement may be a separate attachment, or may be inserted at the bottom of page 3 of the farm application blank. e. liestilction re~ ardinp: l andsopresently owned on any Federal reclamation projects.- In addition, i n order to qualify for entry on project lands, applicants must not hold or own, within any Federal reclamation project, irrigable land for h i c h construction charges payable t o the United States have not been fully paid. Proofs of conformity with t h i s renuirement need not he furnished, but a check of proj-ect lands w i l l be made to determine e l i g i b i l i t y of applicants before, awards of farm units are nade. 5. Principal qualifications required by homestead laws.- Tne homestead laws reouire that an entrynan or entxyvmman: a. Must be a citizen of the United States or have declared an intention to become a citizen of the United Stntes. , . + b. Must not have exhausted the ri& t to make hoxestead entry on plblic land. c. Must not own more than 160 acres of land i n the TJnited States. d. Entrywomen who are married must be heads of families; t h i s requirement of the homestead law was not affected by the Act of September 27, 19WI. ( 58 Stat. 747), as amended. Nntrgmen and unmarried entrywomen must be 21 years of age or the head of a family, except that such minimum age reauirement is not applicable t o entrymen or unmarried entrywomen who have served in the Army, Navy, Marine Corps or Coast Guard of the United States for a period of a t l e a s t 90 days a t any time on or a f t e r September 16, 1940, and prior to the termination of the present war and are honorably discharged. Any applicant who i s renuired t o be the head of a family must submit proof of such status with his or her application. Complete information concerning qualifications for homesteading may be obtained from District Land. Offices or from the Bureau of Land Management, Washington 25, D. C. I 6. .& en. where. and how to amly for a farm unit. a. Application blanks.- Pay person desiring to acauire one of the p b l i c land units described i n t h i s notice must f i l l out the attached farm application blank. Additional application blanks may be obtained from the D i s t r i c t Manager, Bureau of Reclamation, P. 0. Box 312 ( quilding 61, Mmicipal Air-port), Klamath Falls, Oregon; Regional Director, Bureau of Reclamation, P. 0. Yox 25ll, Sacramento 10, California, or the Commissioner, Bureau of Reclamation, Washington 25, D. C. Each question on the farm application blank must be answered completely, with the exception that preference choice of farm units need not be listed i n the space provided on page J. b. Filing of applications and proofs.- An application for a, fann unit l i s t e d in paragraph 1 of t h i s notice must be f i l e d with the District Manager. hreau of Reclamation. P. 0. Box 312, ( Building 61, Municipal Airport), Klamath Falls, Oregon, in persoi or by mail. No advantage will accrue to an appli-- cant who presents h i s or her application i n person. Such an application must be accompanied by: ( I ) Proof of veteran's status i f veteranst nreference i s claimed; see above, paragraph 3 c. ( 2) Three statements as to character and industry; see above, pragraph 4 a. ( 3) statement of examining physician, i n case of disability; see above, praeraph 4 b. ( 4) Three statements corroborating the fanu experience cldm; see above, paragraph 4 c ( 2). ( 5 ) Corroboration of c a p i t a l assets; see above, paragraph 4 d. ( 6) Proof of status a s head of a family I f applicant i s a narried wman veteran, or a non-veteran under the age of 21; see above paragraph 5 d. c. Priority of applications.-- All applications f i l e d f o r the public land fam units l i s t e d i n t h i s notice w i l l be classified for priority purposeseas follows and considered i n the following order: ( 1) First Prioritg- G-.-- All applications fj led prior to 2: 00 p. m., Januarg 20, 1948, 4. which are accompanied by proof sufficient i n the opinion of the board t o establish e l i g i b i l i t y f o r veterans' preference, A l l such applications will be treated as simultaneously filed. ( 2) Second Przorit Grou .-. A11 applications f i l e d prior t o 2: 00 p. m., ~ anuary' 20, 1948, from applicants without veterans: prefzrence o r which are nvt accompanied hy proof sufficient in the ' A opinjon of the board. to establish e l i g i b i l i t y for veterans' preference. A l l such applications w i l l be t ~ e a t e da s simultaneously filed. . ( 3) Final Priority Grou..- All applications f i l e d after 2: 00 p. m., January 20, 1948, whether or not accompanied by proof relative t o veterans' preference. Such applications w i l l be con-sidered in the order i n which they are filed, i f any farm units become available for assignment to appli-cants within t h i s group. d. h l i c a t i o n s cannot be returned.--% ch application subnitted, including substantiating and supporting data, becomes a pert of the pemnent records of the Burem of Reclamation and cannot be returned to the applicant. \ 7. Selection of 2 G f i e d apulicants. a. 7?,, 7minin~ h- o~.-. b examining board of three nemhers has heen approved hy the Commissioner of Reclamation t o consider the fitness of each applicant t o undertake the development and operation of a farm on the Klamath Project. Careful investigations will he made t o verify the statercents and representntions made by .% pplicants in order t o determine t h e i r nualifications as prescribed in t h i s notice. b. Wsis of exami. n& t> s.-- The examinin& hoard will determine the eligibility for the award of a reclamation farm unit under subsection 4C of the Act of December 5, 1924. As stated ahove i n para-graph 4, applicants w i l l be judged on the basis of character, industry, fanning experience, and capital. No applicant w i l l be considered eligible who does not malify i n all respects, or who doe3 not, in the opinion of the board, possess the health and vigor to engage in farm work. Any f a l s i f i c a t i o n or fraudu-lent misrepresentation shall constitute ground for the dismalification of the applicant, the rejection of his application, the cancellation of his award, and/ or the cancellation of his entry. c. Procedure. ( 1) Pre1ivina~~ amination.-- If ah applicant f a i l s to make a prima facie case, that is, i f an ex- mLnation of h i s application discloses that he is not qualified i n respect to the requirements prescribed herein, the application shall be rejected and the applicant notified by the board of such rejection and the reasons therefor, and of h i s right to'appeal in writing to the Regional Director, Region 11, Bureau of Reclamation. Such written appeals must be filed within ten ( 10) days from the receipt of such notice with the District Kanager, Bureau of Reclamation, P. 0. 90x 312 ( Building 61, Municipal Airport), Klamath Falls, Oregon, who will forward them promptly t o the Regional Erector. If an appeal i s decided by the Regional Xrector i n favor of the applicant, the application will be referred to the examining board for inclusion i n the drawing. A l l decision3 on appeals will he based exclusively on information obtained prior t o rejection of the application by the examining board. The Kegional Director's decision on a l l appeals shall be a n a l . ( 2) Selection of a~ plicants.- After the expiration of the anpeal periods fixed by the ahoveaentioned notices, . wd in the absence of any pending appeals, the examining board shall conduct a public drawing from the names of the remaining applicants i n the First Priority Group, as defined i n parapaph 6 c. Qualified applicants need not be present a t the drawing i n order to participate therein. A t o t a l of 88 names ( twice the numher of puhlic land farm units to be awarded) shell be drawn snd numbered consecutively. The applicants whose names are so drawn may be closely investieated by the board to determine the authenticity and r e l i a b i l i t y of the infcnnation and proofs offered by them. This i n v e s t i ~ a t i o nm ay include a personal appearance before the board, i f the hoard determines that t h i s i s necessnry; should any applicant f a i l to com? ly with the hoard's renuest for a personal appearance, such f a i l u r e shall conatitute ground for rejection of his application. Any applicant, whose application is rejected by the board as a result of such investigation, shall he given notice of such rejection, setting forth the reasons therefor and advising the ap licant of his right t o appeal in writing to the Xegional Director. The provisions of paragraph 7 c ( 17 relative t o appeals shall be applicable to any such appeal, except that where any such appeal i s decided by the Regional Director in favor of the applicant such applicant shall retain the number assigned t o him a t the time of the drawing. After the expiration of all appeal periods fixed by notices given as above- provided, and i n - t h e absence of any pending appeals, those applicants whose applications remain unrejected and who hold the W, lowest numbers assigned a t the drawing, exclusive of those numbers assigned to rejected applications, shall be selected by the e x d n i n g board as the successful applicants. The balance of the 88 appli-cants whose applications remain unrejected shall be selected by the board as alternates. The board shall thereupon notify each successful applicant and each alternate of h i s selection and of his respective standing. The board shall thereupon notify a l l other remaining a l i c a n t s t h a t farm units will not becom available to than, except pursuant to subparagraph 7 c. ( 3)( 3bel ow. ( 3) Awarding of farm units. ( a) Upon the completi. on of any action which may become necessary by reason of any notices given, the examining board shall award farm units i n accordance with order of selection numbers assigned such units to the above- mentioned W, successful applicants i n the order in which t h e i r names are drawn without regard to preferences indicated by applicants for specific farm u n i t s o r otherwise. Each applicant to whom a farm unit has been awarded will be notified of t h a t f a c t by the board. Each such applicant shall have no right of entry for any other farm unit. If any such applicants f a i l to make application for homestead entry in conformity with the provisions of paragraph 9 below or t o comply with the other applicable renuircrrmente set out in said paragraph, the farm units awarded to them shall he awarded to alternates i n the order in which t h e i r names were dram and mbjact to the same condi-tions and reouirements as the 01% nal awards. ' he alternate withthe lowest number as assigned under the p= ovisions of paragraph 7 c. $ 1 hall tak( the place of the loweat numbered applicant m n g the f i r s t W* who f a i l s to make application for homestead entry. or disqualifies by failure to comply with the other rerpirmmts s e t forth i n paragraph 9 below; and the alternate with the second lowest number shall take the place of the second lowest numberad applicant who f a i l s t o make application for homestead entry or comply with the other mruiremmtr. Thm same procedure shall continue to apply u n t i l a l l f a n units have been awarded. ( b) The foregoing procedure h a l l continue u n t i l a l l fam units are finally disposed of to unrejected mpplicantr in the First Priority Group whose names have been drawn and whose applica-tions hnve been closely investigatd as provided herein. If units still remain to be awarded a f t e r a l l applications in the Pirst Priority Group have been procerrod, the foregoing procedure shall be applied i n the proceasing of applications in the Second Priority Group. If d t s . till remain t o b e awarded a f t e r all applications in the Second Priorlty Cmup have been processed, the foreg'oing procedure shall be applied in the'processing of applications i n the Pinal Priority Group, except that the board shall consider such applications in the order i n which they are f i l d i n lieu of conducting a drawing with reference thereto. ( 4) DeUmrg of notices.- All notices given to applicants pursuant to the provisions of paraeraph 7 c. and subparagraphs thereunder shall be i n writing and shall be delivered t o the respective applicants personally or sent to them by registered m a i l with return receipt requested. 8. ! Narn- against unlawful settlement.- No parson shall be permitted t o gain or exorcise any right under any settlement or occupation of any of the public lands covered by t h i s notice except under the terms and conditions prescribed by t h i s notice. 9. Payment of charms and filin,? of homestead applications.- After the 44 successful applicants have been selected, they & all be so notified hy the examininl~ board, and with such notice the examining hoard shall enclose a water rental application for the farm unit awarded which must be executed by the applicant and returned to the District Manager, Bureau of Reclamation, P. 0. Box 312 ( Buildiq 61, hnicipal Airport), Klamath Falls, Oregon, within ten ( 10) days from receipt thereof, to& her with the pdyment of the minimum water rental charge as specified i n uaragraph 10 a. hereof. Upon r e c e i ~ to f water rental application and payment of the amount due thereon, the examining board shall furnish each appli-cant a c e r t i f i c a t e statine that his qualifications to enter public lands as renuired by subsection C of Section 4 of the Act of December 5, 1924 ( W Stat. 702) have been uassed upon and approved by the examining board. Such c e r t i f i c a t e mast be attached by the applicant t o h i s homestead application which application must he f i l e d at the District Land Office of the Bureau of Land Management, Sacramento, California. Such homestead application must be f i l e d within t h i r t y ( 30) days from the date of the receipt by the applicant of said certificate. Failure to pay the water rental charge or to make appli-cation for homestead entry within the periods specified herein w l l l render the application subject to rejection, i n which event the examining board w i l l select the next listed alternate. 10. Charges payable by a l l water users,- The Reclamation Law provides that except during a ' ldeveloument ~ eriodl' fixed by the Secretary of the Interior water m y not be delivered for the irrina-tion of- lands- until an org& zation, satisfactory i n form and powers- to the Secretary, has entered into a contract with the United States prodding for the repayment of the project construction costs & ich are allocated to such irrigated lands. Pursuant to Section 2 ( 5 ) and 7 ( b) of the Rsclnmation Project Act, of 1939, ( 53 5tat. 1187), lands described i n paragraph 1 of t h i s plblic notice are hereby designated a developnent unit. The maximu developnent period for the lands so designsted i s fixed a t a period of four gears from and including the f i r s t year in which water i s delivered; provided, that such period may be reduced by supplemental mtice should the Secretary determine that the f u l l four- year period i s not reasonably necessarg. Before the end of tha developent period, a l l lands described i n said para-graph 1, must, therefore, be included within an organization of the type described and such organization must execute a contract cwering the repaynent of the construction costs allocated to such lands. a. Char~ es payable before execution of the r e p s p n t contract. ( 1) The minimum water rental charge f o r the irrigation season of 1948 and thereafter u n t i l further notice shall be three dollars ($ 3.00) per acre for each irrigable acre of land in the f a n unit, whether water i s used or not, which will entitle the entryman to two and one half ( a) acre- feet . of water per irrigable acre. Payment of this charge for the irrigation season of 1948 s h a l l be made at the time of filing water rental applications. ( 2) Additional water dl1 be firnished during the 1948 i r r i ~ a t i o n season and thereafter u n t i l further notice up to a limit of three and one half ( 33) acre- feet per irrieable acre at the rate of f i f t y cents ( 80.50) per acre- foot and a11 further nuantities a t seventy- five cents ( w. 75) per acre-foot. Charges for the additional water are to be paid on or before hcember 1 of the year in which used. No water shall be delivered to the water uemr in mbsequent years u n t i l a l l such charges have been paid in full. ( 3) In the event any applicant does not receive notice of the award of a farm unit u n t i l a f t e r June 15, 1948, payment shall be a minimum charge of three dollars ($ 3.00) per acre, which payment shall apply as a credit on the minimum charge for the following irrieation season. ( h) The foregoing charges are subject t o a l l provisions of the Federal Reclamation Law relative to collections and penalties for delinquencies. The charges w i l l be paid a t the office of the Bureau of Reclamation, Klamath Falls, Oregon. Future charges dll be announced by future order o r public notice. 6. b. Charges payable a f t e r execution of the repayment contract.- Subsequent to the execution of the repayment contract, and i n accordance with the terms thereof, water users will pay an annual charge per acre t o meet operation and maintenance costs and t o repay t o the government that portion of the constmction costs allocated to Part 2, Tule Lake Division. On the date of issue of t h i s puhlic notice, it i s impracticablr to determine ( 1) the t o t a l construction cost of Part 2, Tule Iake Divlsion distributary system; ( 2) the allocation of costs to Part 2, ' We Lake Division of tho Klamath Federal Reclamation Pmject, and ( 3) the ultimate water- service area of the Division. Accorrlingly, no exact statmnent as t o the t o t a l and per acre construction charge t o be made against the lands opened in t h i s puhlic notice i s practicable, When the t o t a l construction charge has been detedned and allocated by the Secretary of the Interior, and a repapent c o n t r q ~ tn egotiated with the irrigation d i s t r i c t , a supplementary notice announcing the t o t a l and per acre charges will be issued. 11. A l l land to be i ~ c l u d e di ~- i- r1ii~ t~ qnn( 1- i= t_~ i~.- 5acwh ater rental appliciltion for land covered by t h i s plblic notice shall be made on Form 7- 39 and the followine clause shall be inserted a5 the bottom of wid form: " 1 agree to the inclusion of my land i n an irrigation d i s t r i c t and I agree'also to p r t i c i p a t e in the organization of ? n i r r i ~ a t i o nd i s t r i c t at the earliest practicable date." 12. Reservation of riphts- of- way for county. state. and Federal highwzys and access roads.- Rights- of- way are reserved for county, s t a t e and Federal highways and access roads to the f ~ r mu nits shown on said plats along section lines and other lines shown in red on the farm plats. 13. Reservation of ri& ts- of- wau for publicdwned utilities.- Kightsdf- way are reserved for covernment- owned telephone, electric transmission, water and sewer lines, and water treating and pump ing plants, as now constructed, a d the secretary of the Interior reserves the r i g h t t o locate such other gwenwent- owned f a c i l i t i e s over and across the farm units above descri! md as hereafter, i n his opinion, may be necessary f o r the proper construction, operation, and maintenance of the said project. 14. Effect of relinquishment.-- In tho event that any entry of public land made hereunder shall be' relinauished ot any time prior to actual residence upon the land by the entrynan for not less than one year, the land so relinquished shall not be subject to entry for a period of 60 days a f t e r the f i l i n g and nctation of the relinnuishment i n " he Cistrict Land Office. Applicfltions conforming to the reqhire-ments of t h i s public notice may be f i l e d for a period of 15 days a f t e r the expiration of said 60- day period. Ach applications w i l l be considered ard processed anrl awards made pursuant to the provisions of paragraphs 7 and 9 of this public notice. 15. Waiver of mineral rights.-- All homestead entries f o r the ahove- described farm units will he subject to the laws of the United States governing mineral land, and all homestead applicarts under this notice must waive the rij< ht t o the mineral content of the land, i f required to do so by tke hrea. 1 of Lwd Ifanagement; otherwise the homestead applications will he rnjected o r the homestead entry or entries canceled. 16. Flood hazard.-- The lands to he entered are reclaimed lands lyiw in the former bed of Tnle Lake and m y be subject t o flooding and invndation during extremely wet nesrs. The Sureau of 2ecla1rstion i s now engaged i n the constmction of additionel works which, when completed, w i l l nrov5. de reasonnble flood protection. Settlers are warned, however, that i n case- of extreme mnoff result in^ in the fl. ood-iny of any of the lands, the government assumes no responsitdlity for dmare to persons or property caused by such flooding. Assistant Secretary of the Interior Title: Public notice opening public lands to entry and announcing availability of water therefor : Public notice no. 45, October 8, 1947, Klamath Project Oregon-California, Part 2 - Tule Lake Division Author: United States. Bureau of Reclamation Year: 1947, 2005, 2004 UNITED STATES DEPAXTMENT OF. THE INTERIOR BUREAU OF RECLAMATION Washington, D. C. Public Notice No. I45 October 8, 1947 KLAMATH PROJECT, OREMN - CALIFORNIA PAXT 2- TLILE LAKE DIVISION PUBLIC NOTICE OPENING PUBLIC LANDS TO ENTRY AND ANNOUNCING AVAILABILITY OF WATER THRWOR 1. Public land for vhich water i s available and for + ich entry may be made.-- In pursuance of the Act of June 17, 1902 ( 32 Stat. 388) and acts amendatory thereof or supplementary thereto, it i s hereby announced that water w i l l be available beginning with the i r r i ~ a t i o ns eason of 1948, end thereafter, and that application may be made in accordance with t h i s notice, beeinnine a t 2: 00 p. m., October 22, 1947, for entry on public lands i n Part 2- file Lake Division of the KlamAth Project,, Oregon - California, as shown on approved farm unit plats on f i l e in the Office of the District Manaaer. Bureau of Reclamation. Klamath Falls. Oregon. and in the District Land Office a t Sacramento, ~ a l i r o r k a . These lands are dkcribed as fofiows:- . Mount Diablo Meridian. California Section 1 36 1 1 1 1 1 1 1 2 1 2 2 2 3 2 3 2 2 2 1 11 12 1 11 11 - Farm - Unit A B C D E F G H J A B C D E F K L A B Description Township 46 North. Ranp( e 5 % st Lots 1, 8 & ~"$ IE& ( T. C7 N., R. 5 E.) Lo* 10 Lots 2, 7 & 9 i ~ t ~ & Lots 3, 6 & SEN& Lots 12 and 15 Lot 18 ~ 4 SWk ~ 4 % E& E& Lots 4 & 5 Lots 13 & 14 ~ o1t & NNE~ Lot 2 & SE& NW~ Lot 3 Lot 20 swl. Srwt Lot 22 E!& '& a h t s 6 & 7 Lots 16 & 17 Lots 4 & 5 Lot 6 Lot 19 ww4 @ NWt Total Irri-gable Acres 86.7 81.9 84.6 84.2 72.9 73.8 71.4 72.0 n. 4 73.5 73.4 84.0 86.6 * 77.3 75.5' n. 8 68.8 75.2 Order of Selection Section 11 u 11 ll 12 12 12 12 12 12 12 12 12 35 35 34 35 34 35 35 36 36 6 6 7 6 7 7 7 - Farm - Unit C D E J A B C D E F G H A B C D i3 B C A B C A B D Total Irri- Description gable Acres Township 46 North. Rawe 5 East( contd. 1 L c t s 6 & 7 Lots 7 & 8 Lot 9 Township 427eh. Range 5 East Lots 12 & 13 Lots 11 & 14 Lot 9 $ 94 Lot 10 Lot 3 w& i Lots 4, 8 & 9 Township 46 North. Range 6 East Lcts 15, 16 & 18 Lots 6, 10, 17, 20 & 21 Lots 15, 16, Lots 22 & 23 Lots 7, 11, 17, 18, SZ$ NI+~ Lots 8, 12 & NE$ SW& Lots 9, U & sE$& Order of - Sslection 2. & nit of acreaKe for which entry may be made or water secured.-? he area of public land constituting each farm unit represents the acreage which, in the opinion of the Secretary of the Interior, may be reasonably reouired for the support of a family upon such land, and i s fixed a t the amount shown upon the farm unit plats referrcd to above. 3. Preference rinhts of veterans. Nature of reference.-- Pursuant to the provisions of the A- ct of September 27, 1944 ( 58 Stat. ai47>- dyt?;;; Acts of June 25, 1946 ( Public Law 440, 79th Congress, 2nd ~ e s s i o n ) , and May 31, 1947 ( Public Law 82, 80th Congress, 1st session), for a period of 90 days from the opening of these lands to entry, or u n t i l January 20, 1948, the lands described i n paragraph 1 above w i l l be opened t o entry to persons who a t the time of milking application f a l l within one of the following classes: ( 1) Persons, including persons under 21 years of age, who have served i n the Army, Navy, Marine Corps, or Coast Guard of the United States for a period of a t l e a s t 90 days a t any time on o r a f t e r September 16, 1940, and prior to the termination of the present war, and are honorably discharged therefrom. ( 2) Persons, including persons under 21 years of age, who have served i n said Amy, Nairy, Marine Corps or Coast Guard during such period, regardless of l e n ~ t ho f service, and are discharged on account of wounds received or disability incurred during such period i n the line of duty, or, subsequent t o a regular discharge, are furnished hospitalization or awarded compensation by the government on account of such wounds or disability. ( 3) Ihe spouse of any person i n e i t h e r of the above classes ( 1) and ( 2), provided such spouse has the consent of such person to exercise his o r her preference right under said Act. ( L) The surviving spouse of any person i n either of the above classes ( 1) and ( 2), or i n the case of the death or marriage of such spouse, the minor child or children of such person by a guardian duly appointed and o f f i c i a l l y accredited a t the Department of the Interior, ( 5) The surviving spouse of m p person whose death has resulted from wunds received or disability incurred i n l i n e of duty while s e r v i n ~ i n said Army, Navy, Marine Corps or Coast , Tuard during the aboveaentioned period, or i n the case of the death or mrriage of such spouse, the oinor child or children of such person by a guardian duly appointed and o f f i c i a l l y accreEited a t tile Department of the Interior. Provided, however, that persons claiming such preferences must be qualified t o make entry under the homestead laws and also possess the qualifications as t o industw, experience, character, capital, and physical fitness required of a l l entrymen and entrywomen under t h i s notice. b. Definition of honorable discharge.- An honorable discharge within the meaning of the Act of Septenber 27, 1964, as amended, shall mean: ( 1) Separation of the veteran from the service by means of an honorable discharge or a discharge under honorable conditions. ( 2) Transfer of the veteran with honorable service from such service to a reserve or r e t i r e d s t a t u s prior to the termination of the war, or ( 3) Ending of the period of such veteran's war service by reason of the temination of the war, even though the veteran remains i n the military or naval service of the United States. c. Submission of proof of veterans' status.- All applicants for farm units who claim veterans* preference must attach to t h e i r applications a photostatic, c e r t i f i e d , or authenticated copy of an o f f i c i a l document of the respective branch of the service involved which clearly indicates an honorable discharge or transfer to a reserve o r retired status or which constitutes eddence of other facts on which the claim for preference i's based. Where the preference i s claimed by the surviving spouse, or on behalf of the minor child or children, of a deceased veteran, proof of such relationship, of his military service, and of his death must be attached to the application. Where the preference i s claimed by the spouse of a livinz veteran, proof of such relationship, the written consent of such veteran, and proof of his military service as re, mired above must be attached to the application. 4. Qualifications required by the Reclamation Law.-- Pursuant to the provisions of subsection C, section I+. of the Act of December 5. 1924 ( L3 Stat. 702. 43 U. S. C. 433). the follow in^ are established as minimrun nualifications which, in'the opinion of the iocal examjning koe. rd, are necessary to insure the success of entrymen or entrywomen on reclamation farm units included under t h i s notice. Appli-cants must meet these qualifications, as determined by the exanAninc boerd, i n order to he considered for entry. Failure to meet them i n any single respect will be sufficient cause for rejection of an application. No credit wi'll be given : or qualifications i n excess of the minimum reouired. The minimum qualifications are as follows: l a. Character and industry.- The applicant must be possessed of honesty, temperate habits, t h r i f t , industry, seriousness of purpose, record of good moral conduct, an8 a bona f i d e i n t e n t t o engage in farming as an occupation. As part of each application, the applicant shall furnlsh three separate signed statements regarding the character and industry of the applicant. These statements may be prepared and signed by an ordained sinister, any commanding officer under whom the applicant served, a teacher or administrative o f f i c i a l of any recognized high school o r college, present or previous employer or any comparable individual or o f f i c i a l , not a relative, who i s personally acquainted with the applicant. The individuals signing these statements may be those l i s t e d in para-graph 17 of the farm application blank, referred to i n paragraph 6 of t h i s notice. \ b. Health.-- The applicant must be i n such physical condition as w i l l enable him t o engage i n n o m l farm labor. Any person who i s physically handicapped or afflicted with any condition which makes such a b i l i t y questionable must attach to his application the detailed statement of an examining physician which defines the limitation upon such a b i l i t y and i t s causes. c. Farm experienn. ( 1) Fam experience shall be of such a n a t ~ r ea s in the judgment of the examining board w i l l qualify the applicant to undertake the development and operation of an irrigated farm by modern methods. The applicmt must have had a minimum of twa years' full- time farm experience a f t e r attain-ing the age of 15 years. ' Iko years of study i n agricultural courses i n an accredited agricultural college or tw years of responsible technical work in agriculture, i f deemed by the examining board to be work which would contlribute toward successful farm operation, may be substituted for one year of full- time experience; pmvided that no more thnn one year's experience may be credited from such sources. . A farm youth having atteined the age of 15, who actually resided and wrked on a farm h i l e attending school, majr credit such part- time experience as equal to 50 percent of full- time experience. A l l fam experience must have been obtained since October 1, 1932. No advantage w i l l accrue from farming ex-perienae on irrigated land. ( 2) Applicants must furnish three separate statements each signed either by a Vocational Agricultural teacher, County Agent, Farmers Home Administration County Supervisor, A. A. A. County Chairman, an officer of any local farm organization, or by some other responsible person who has personal knowled~ e of the applicant's farm experience or has verified it to h i s satisfaction certifying t o the farm experience claimed i n paragraph 7 of the farm application blank. Forms to be used by these references accompany each farm application blank. ( 3) Women applicants must describe fully the farm a c t i v i t i e s i n which they have participated and the relation of any agricultural courses they have taken to farm operation and management. d. Capital.-- Each applicant must possess at least $ 2,000, consisting of cash or assets readily convertible into cash, such as United jtates Savings Bonds, or assets useful i n the operation of a fann, such as livestock, farm machinery and equipent. In addition, each applicant shall furnish, i n the space pmvided i n paragraph 11 of the farm application blank, a financial statement l i s t i n g all of h i s assets and all of h i s l i a b i l i t i e s , showing a net worth of a t l e a s t 92,000. " Possession of the minimum net Worth rewrement of at least $ 2,000 must be corroborated hy a statement of an o f f i c i a l of a bank, or other responsible and reputable private or public credit agency. This corroborative statement may be a separate attachment, or may be inserted at the bottom of page 3 of the farm application blank. e. liestilction re~ ardinp: l andsopresently owned on any Federal reclamation projects.- In addition, i n order to qualify for entry on project lands, applicants must not hold or own, within any Federal reclamation project, irrigable land for h i c h construction charges payable t o the United States have not been fully paid. Proofs of conformity with t h i s renuirement need not he furnished, but a check of proj-ect lands w i l l be made to determine e l i g i b i l i t y of applicants before, awards of farm units are nade. 5. Principal qualifications required by homestead laws.- Tne homestead laws reouire that an entrynan or entxyvmman: a. Must be a citizen of the United States or have declared an intention to become a citizen of the United Stntes. , . + b. Must not have exhausted the ri& t to make hoxestead entry on plblic land. c. Must not own more than 160 acres of land i n the TJnited States. d. Entrywomen who are married must be heads of families; t h i s requirement of the homestead law was not affected by the Act of September 27, 19WI. ( 58 Stat. 747), as amended. Nntrgmen and unmarried entrywomen must be 21 years of age or the head of a family, except that such minimum age reauirement is not applicable t o entrymen or unmarried entrywomen who have served in the Army, Navy, Marine Corps or Coast Guard of the United States for a period of a t l e a s t 90 days a t any time on or a f t e r September 16, 1940, and prior to the termination of the present war and are honorably discharged. Any applicant who i s renuired t o be the head of a family must submit proof of such status with his or her application. Complete information concerning qualifications for homesteading may be obtained from District Land. Offices or from the Bureau of Land Management, Washington 25, D. C. I 6. .& en. where. and how to amly for a farm unit. a. Application blanks.- Pay person desiring to acauire one of the p b l i c land units described i n t h i s notice must f i l l out the attached farm application blank. Additional application blanks may be obtained from the D i s t r i c t Manager, Bureau of Reclamation, P. 0. Box 312 ( quilding 61, Mmicipal Air-port), Klamath Falls, Oregon; Regional Director, Bureau of Reclamation, P. 0. Yox 25ll, Sacramento 10, California, or the Commissioner, Bureau of Reclamation, Washington 25, D. C. Each question on the farm application blank must be answered completely, with the exception that preference choice of farm units need not be listed i n the space provided on page J. b. Filing of applications and proofs.- An application for a, fann unit l i s t e d in paragraph 1 of t h i s notice must be f i l e d with the District Manager. hreau of Reclamation. P. 0. Box 312, ( Building 61, Municipal Airport), Klamath Falls, Oregon, in persoi or by mail. No advantage will accrue to an appli-- cant who presents h i s or her application i n person. Such an application must be accompanied by: ( I ) Proof of veteran's status i f veteranst nreference i s claimed; see above, paragraph 3 c. ( 2) Three statements as to character and industry; see above, pragraph 4 a. ( 3) statement of examining physician, i n case of disability; see above, praeraph 4 b. ( 4) Three statements corroborating the fanu experience cldm; see above, paragraph 4 c ( 2). ( 5 ) Corroboration of c a p i t a l assets; see above, paragraph 4 d. ( 6) Proof of status a s head of a family I f applicant i s a narried wman veteran, or a non-veteran under the age of 21; see above paragraph 5 d. c. Priority of applications.-- All applications f i l e d f o r the public land fam units l i s t e d i n t h i s notice w i l l be classified for priority purposeseas follows and considered i n the following order: ( 1) First Prioritg- G-.-- All applications fj led prior to 2: 00 p. m., Januarg 20, 1948, 4. which are accompanied by proof sufficient i n the opinion of the board t o establish e l i g i b i l i t y f o r veterans' preference, A l l such applications will be treated as simultaneously filed. ( 2) Second Przorit Grou .-. A11 applications f i l e d prior t o 2: 00 p. m., ~ anuary' 20, 1948, from applicants without veterans: prefzrence o r which are nvt accompanied hy proof sufficient in the ' A opinjon of the board. to establish e l i g i b i l i t y for veterans' preference. A l l such applications w i l l be t ~ e a t e da s simultaneously filed. . ( 3) Final Priority Grou..- All applications f i l e d after 2: 00 p. m., January 20, 1948, whether or not accompanied by proof relative t o veterans' preference. Such applications w i l l be con-sidered in the order i n which they are filed, i f any farm units become available for assignment to appli-cants within t h i s group. d. h l i c a t i o n s cannot be returned.--% ch application subnitted, including substantiating and supporting data, becomes a pert of the pemnent records of the Burem of Reclamation and cannot be returned to the applicant. \ 7. Selection of 2 G f i e d apulicants. a. 7?,, 7minin~ h- o~.-. b examining board of three nemhers has heen approved hy the Commissioner of Reclamation t o consider the fitness of each applicant t o undertake the development and operation of a farm on the Klamath Project. Careful investigations will he made t o verify the statercents and representntions made by .% pplicants in order t o determine t h e i r nualifications as prescribed in t h i s notice. b. Wsis of exami. n& t> s.-- The examinin& hoard will determine the eligibility for the award of a reclamation farm unit under subsection 4C of the Act of December 5, 1924. As stated ahove i n para-graph 4, applicants w i l l be judged on the basis of character, industry, fanning experience, and capital. No applicant w i l l be considered eligible who does not malify i n all respects, or who doe3 not, in the opinion of the board, possess the health and vigor to engage in farm work. Any f a l s i f i c a t i o n or fraudu-lent misrepresentation shall constitute ground for the dismalification of the applicant, the rejection of his application, the cancellation of his award, and/ or the cancellation of his entry. c. Procedure. ( 1) Pre1ivina~~ amination.-- If ah applicant f a i l s to make a prima facie case, that is, i f an ex- mLnation of h i s application discloses that he is not qualified i n respect to the requirements prescribed herein, the application shall be rejected and the applicant notified by the board of such rejection and the reasons therefor, and of h i s right to'appeal in writing to the Regional Director, Region 11, Bureau of Reclamation. Such written appeals must be filed within ten ( 10) days from the receipt of such notice with the District Kanager, Bureau of Reclamation, P. 0. 90x 312 ( Building 61, Municipal Airport), Klamath Falls, Oregon, who will forward them promptly t o the Regional Erector. If an appeal i s decided by the Regional Xrector i n favor of the applicant, the application will be referred to the examining board for inclusion i n the drawing. A l l decision3 on appeals will he based exclusively on information obtained prior t o rejection of the application by the examining board. The Kegional Director's decision on a l l appeals shall be a n a l . ( 2) Selection of a~ plicants.- After the expiration of the anpeal periods fixed by the ahoveaentioned notices, . wd in the absence of any pending appeals, the examining board shall conduct a public drawing from the names of the remaining applicants i n the First Priority Group, as defined i n parapaph 6 c. Qualified applicants need not be present a t the drawing i n order to participate therein. A t o t a l of 88 names ( twice the numher of puhlic land farm units to be awarded) shell be drawn snd numbered consecutively. The applicants whose names are so drawn may be closely investieated by the board to determine the authenticity and r e l i a b i l i t y of the infcnnation and proofs offered by them. This i n v e s t i ~ a t i o nm ay include a personal appearance before the board, i f the hoard determines that t h i s i s necessnry; should any applicant f a i l to com? ly with the hoard's renuest for a personal appearance, such f a i l u r e shall conatitute ground for rejection of his application. Any applicant, whose application is rejected by the board as a result of such investigation, shall he given notice of such rejection, setting forth the reasons therefor and advising the ap licant of his right t o appeal in writing to the Xegional Director. The provisions of paragraph 7 c ( 17 relative t o appeals shall be applicable to any such appeal, except that where any such appeal i s decided by the Regional Director in favor of the applicant such applicant shall retain the number assigned t o him a t the time of the drawing. After the expiration of all appeal periods fixed by notices given as above- provided, and i n - t h e absence of any pending appeals, those applicants whose applications remain unrejected and who hold the W, lowest numbers assigned a t the drawing, exclusive of those numbers assigned to rejected applications, shall be selected by the e x d n i n g board as the successful applicants. The balance of the 88 appli-cants whose applications remain unrejected shall be selected by the board as alternates. The board shall thereupon notify each successful applicant and each alternate of h i s selection and of his respective standing. The board shall thereupon notify a l l other remaining a l i c a n t s t h a t farm units will not becom available to than, except pursuant to subparagraph 7 c. ( 3)( 3bel ow. ( 3) Awarding of farm units. ( a) Upon the completi. on of any action which may become necessary by reason of any notices given, the examining board shall award farm units i n accordance with order of selection numbers assigned such units to the above- mentioned W, successful applicants i n the order in which t h e i r names are drawn without regard to preferences indicated by applicants for specific farm u n i t s o r otherwise. Each applicant to whom a farm unit has been awarded will be notified of t h a t f a c t by the board. Each such applicant shall have no right of entry for any other farm unit. If any such applicants f a i l to make application for homestead entry in conformity with the provisions of paragraph 9 below or t o comply with the other applicable renuircrrmente set out in said paragraph, the farm units awarded to them shall he awarded to alternates i n the order in which t h e i r names were dram and mbjact to the same condi-tions and reouirements as the 01% nal awards. ' he alternate withthe lowest number as assigned under the p= ovisions of paragraph 7 c. $ 1 hall tak( the place of the loweat numbered applicant m n g the f i r s t W* who f a i l s to make application for homestead entry. or disqualifies by failure to comply with the other rerpirmmts s e t forth i n paragraph 9 below; and the alternate with the second lowest number shall take the place of the second lowest numberad applicant who f a i l s t o make application for homestead entry or comply with the other mruiremmtr. Thm same procedure shall continue to apply u n t i l a l l f a n units have been awarded. ( b) The foregoing procedure h a l l continue u n t i l a l l fam units are finally disposed of to unrejected mpplicantr in the First Priority Group whose names have been drawn and whose applica-tions hnve been closely investigatd as provided herein. If units still remain to be awarded a f t e r a l l applications in the Pirst Priority Group have been procerrod, the foregoing procedure shall be applied i n the proceasing of applications in the Second Priority Group. If d t s . till remain t o b e awarded a f t e r all applications in the Second Priorlty Cmup have been processed, the foreg'oing procedure shall be applied in the'processing of applications i n the Pinal Priority Group, except that the board shall consider such applications in the order i n which they are f i l d i n lieu of conducting a drawing with reference thereto. ( 4) DeUmrg of notices.- All notices given to applicants pursuant to the provisions of paraeraph 7 c. and subparagraphs thereunder shall be i n writing and shall be delivered t o the respective applicants personally or sent to them by registered m a i l with return receipt requested. 8. ! Narn- against unlawful settlement.- No parson shall be permitted t o gain or exorcise any right under any settlement or occupation of any of the public lands covered by t h i s notice except under the terms and conditions prescribed by t h i s notice. 9. Payment of charms and filin,? of homestead applications.- After the 44 successful applicants have been selected, they & all be so notified hy the examininl~ board, and with such notice the examining hoard shall enclose a water rental application for the farm unit awarded which must be executed by the applicant and returned to the District Manager, Bureau of Reclamation, P. 0. Box 312 ( Buildiq 61, hnicipal Airport), Klamath Falls, Oregon, within ten ( 10) days from receipt thereof, to& her with the pdyment of the minimum water rental charge as specified i n uaragraph 10 a. hereof. Upon r e c e i ~ to f water rental application and payment of the amount due thereon, the examining board shall furnish each appli-cant a c e r t i f i c a t e statine that his qualifications to enter public lands as renuired by subsection C of Section 4 of the Act of December 5, 1924 ( W Stat. 702) have been uassed upon and approved by the examining board. Such c e r t i f i c a t e mast be attached by the applicant t o h i s homestead application which application must he f i l e d at the District Land Office of the Bureau of Land Management, Sacramento, California. Such homestead application must be f i l e d within t h i r t y ( 30) days from the date of the receipt by the applicant of said certificate. Failure to pay the water rental charge or to make appli-cation for homestead entry within the periods specified herein w l l l render the application subject to rejection, i n which event the examining board w i l l select the next listed alternate. 10. Charges payable by a l l water users,- The Reclamation Law provides that except during a ' ldeveloument ~ eriodl' fixed by the Secretary of the Interior water m y not be delivered for the irrina-tion of- lands- until an org& zation, satisfactory i n form and powers- to the Secretary, has entered into a contract with the United States prodding for the repayment of the project construction costs & ich are allocated to such irrigated lands. Pursuant to Section 2 ( 5 ) and 7 ( b) of the Rsclnmation Project Act, of 1939, ( 53 5tat. 1187), lands described i n paragraph 1 of t h i s plblic notice are hereby designated a developnent unit. The maximu developnent period for the lands so designsted i s fixed a t a period of four gears from and including the f i r s t year in which water i s delivered; provided, that such period may be reduced by supplemental mtice should the Secretary determine that the f u l l four- year period i s not reasonably necessarg. Before the end of tha developent period, a l l lands described i n said para-graph 1, must, therefore, be included within an organization of the type described and such organization must execute a contract cwering the repaynent of the construction costs allocated to such lands. a. Char~ es payable before execution of the r e p s p n t contract. ( 1) The minimum water rental charge f o r the irrigation season of 1948 and thereafter u n t i l further notice shall be three dollars ($ 3.00) per acre for each irrigable acre of land in the f a n unit, whether water i s used or not, which will entitle the entryman to two and one half ( a) acre- feet . of water per irrigable acre. Payment of this charge for the irrigation season of 1948 s h a l l be made at the time of filing water rental applications. ( 2) Additional water dl1 be firnished during the 1948 i r r i ~ a t i o n season and thereafter u n t i l further notice up to a limit of three and one half ( 33) acre- feet per irrieable acre at the rate of f i f t y cents ( 80.50) per acre- foot and a11 further nuantities a t seventy- five cents ( w. 75) per acre-foot. Charges for the additional water are to be paid on or before hcember 1 of the year in which used. No water shall be delivered to the water uemr in mbsequent years u n t i l a l l such charges have been paid in full. ( 3) In the event any applicant does not receive notice of the award of a farm unit u n t i l a f t e r June 15, 1948, payment shall be a minimum charge of three dollars ($ 3.00) per acre, which payment shall apply as a credit on the minimum charge for the following irrieation season. ( h) The foregoing charges are subject t o a l l provisions of the Federal Reclamation Law relative to collections and penalties for delinquencies. The charges w i l l be paid a t the office of the Bureau of Reclamation, Klamath Falls, Oregon. Future charges dll be announced by future order o r public notice. 6. b. Charges payable a f t e r execution of the repayment contract.- Subsequent to the execution of the repayment contract, and i n accordance with the terms thereof, water users will pay an annual charge per acre t o meet operation and maintenance costs and t o repay t o the government that portion of the constmction costs allocated to Part 2, Tule Lake Division. On the date of issue of t h i s puhlic notice, it i s impracticablr to determine ( 1) the t o t a l construction cost of Part 2, Tule Iake Divlsion distributary system; ( 2) the allocation of costs to Part 2, ' We Lake Division of tho Klamath Federal Reclamation Pmject, and ( 3) the ultimate water- service area of the Division. Accorrlingly, no exact statmnent as t o the t o t a l and per acre construction charge t o be made against the lands opened in t h i s puhlic notice i s practicable, When the t o t a l construction charge has been detedned and allocated by the Secretary of the Interior, and a repapent c o n t r q ~ tn egotiated with the irrigation d i s t r i c t , a supplementary notice announcing the t o t a l and per acre charges will be issued. 11. A l l land to be i ~ c l u d e di ~- i- r1ii~ t~ qnn( 1- i= t_~ i~.- 5acwh ater rental appliciltion for land covered by t h i s plblic notice shall be made on Form 7- 39 and the followine clause shall be inserted a5 the bottom of wid form: " 1 agree to the inclusion of my land i n an irrigation d i s t r i c t and I agree'also to p r t i c i p a t e in the organization of ? n i r r i ~ a t i o nd i s t r i c t at the earliest practicable date." 12. Reservation of riphts- of- way for county. state. and Federal highwzys and access roads.- Rights- of- way are reserved for county, s t a t e and Federal highways and access roads to the f ~ r mu nits shown on said plats along section lines and other lines shown in red on the farm plats. 13. Reservation of ri& ts- of- wau for publicdwned utilities.- Kightsdf- way are reserved for covernment- owned telephone, electric transmission, water and sewer lines, and water treating and pump ing plants, as now constructed, a d the secretary of the Interior reserves the r i g h t t o locate such other gwenwent- owned f a c i l i t i e s over and across the farm units above descri! md as hereafter, i n his opinion, may be necessary f o r the proper construction, operation, and maintenance of the said project. 14. Effect of relinquishment.-- In tho event that any entry of public land made hereunder shall be' relinauished ot any time prior to actual residence upon the land by the entrynan for not less than one year, the land so relinquished shall not be subject to entry for a period of 60 days a f t e r the f i l i n g and nctation of the relinnuishment i n " he Cistrict Land Office. Applicfltions conforming to the reqhire-ments of t h i s public notice may be f i l e d for a period of 15 days a f t e r the expiration of said 60- day period. Ach applications w i l l be considered ard processed anrl awards made pursuant to the provisions of paragraphs 7 and 9 of this public notice. 15. Waiver of mineral rights.-- All homestead entries f o r the ahove- described farm units will he subject to the laws of the United States governing mineral land, and all homestead applicarts under this notice must waive the rij< ht t o the mineral content of the land, i f required to do so by tke hrea. 1 of Lwd Ifanagement; otherwise the homestead applications will he rnjected o r the homestead entry or entries canceled. 16. Flood hazard.-- The lands to he entered are reclaimed lands lyiw in the former bed of Tnle Lake and m y be subject t o flooding and invndation during extremely wet nesrs. The Sureau of 2ecla1rstion i s now engaged i n the constmction of additionel works which, when completed, w i l l nrov5. de reasonnble flood protection. Settlers are warned, however, that i n case- of extreme mnoff result in^ in the fl. ood-iny of any of the lands, the government assumes no responsitdlity for dmare to persons or property caused by such flooding. Assistant Secretary of the Interior Close

• 18. [Image] Draft upper Williamson River Watershed assessment

  	"Prepared for Klamath Basin Ecosystem Foundation, and the Upper Williamson River Catchment Group, in cooperation with the Upper Klamath Basin Working Group, and the Klamath Watershed Council."
  	Citation × Citation Citation Abstract Copy Title: Draft upper Williamson River Watershed assessment Author: David Evans and Associates, Inc. Year: 2004, 2005 "Prepared for Klamath Basin Ecosystem Foundation, and the Upper Williamson River Catchment Group, in cooperation with the Upper Klamath Basin Working Group, and the Klamath Watershed Council." Title: Draft upper Williamson River Watershed assessment Author: David Evans and Associates, Inc. Year: 2004, 2005 "Prepared for Klamath Basin Ecosystem Foundation, and the Upper Williamson River Catchment Group, in cooperation with the Upper Klamath Basin Working Group, and the Klamath Watershed Council." Close

• 19. [Image] Western water supply : hearing before the Committee on Energy and Natural Resources, United States Senate, One Hundred Eighth Congress, second session, to receive testimony regarding water supply issues in the arid West, March 9, 2004

  	CONTENTS STATEMENTS Page American Farm Bureau Federation 26963 Bell, Craig, Executive Director, Western States Water Council 26945 Domenici, Hon. Pete V., U.S. Senator From New Mexico 2691 Gaibler, Floyd, ...
  	Citation × Citation Citation Abstract Copy Title: Western water supply : hearing before the Committee on Energy and Natural Resources, United States Senate, One Hundred Eighth Congress, second session, to receive testimony regarding water supply issues in the arid West, March 9, 2004 Author: United States. Congress. Senate. Committee on Energy and Natural Resources Year: 2004, 2005 CONTENTS STATEMENTS Page American Farm Bureau Federation 26963 Bell, Craig, Executive Director, Western States Water Council 26945 Domenici, Hon. Pete V., U.S. Senator From New Mexico 2691 Gaibler, Floyd, Deputy Undersecretary for Farm and Foreign Agricultural Services, Department of Agriculture 26932 Grisoli, Brigadier General William T., Commander, Northwestern Division, U.S. Army Corps of Engineers 26918 Hall, Tex G., President, National Congress of American Indians, and Chair man, Mandan, Hidatsa and Arikara Nation 26950 Raley, Bennett, Assistant Secretary, Department of the Interior 2695 Uccellini, Dr. Louis, Director, National Centers for Environmental Prediction, National Oceanic and Atmospheric Administration 26926 APPENDIX Responses to additional questions 2620 67 Title: Western water supply : hearing before the Committee on Energy and Natural Resources, United States Senate, One Hundred Eighth Congress, second session, to receive testimony regarding water supply issues in the arid West, March 9, 2004 Author: United States. Congress. Senate. Committee on Energy and Natural Resources Year: 2004, 2005 CONTENTS STATEMENTS Page American Farm Bureau Federation 26963 Bell, Craig, Executive Director, Western States Water Council 26945 Domenici, Hon. Pete V., U.S. Senator From New Mexico 2691 Gaibler, Floyd, Deputy Undersecretary for Farm and Foreign Agricultural Services, Department of Agriculture 26932 Grisoli, Brigadier General William T., Commander, Northwestern Division, U.S. Army Corps of Engineers 26918 Hall, Tex G., President, National Congress of American Indians, and Chair man, Mandan, Hidatsa and Arikara Nation 26950 Raley, Bennett, Assistant Secretary, Department of the Interior 2695 Uccellini, Dr. Louis, Director, National Centers for Environmental Prediction, National Oceanic and Atmospheric Administration 26926 APPENDIX Responses to additional questions 2620 67 Close

• 20. [Image] Weather based technologies for residential irrigation scheduling: technical review report: prepared for Municipal Water District

  	"May 2004"
  	Citation × Citation Citation Abstract Copy Title: Weather based technologies for residential irrigation scheduling: technical review report: prepared for Municipal Water District Year: 2004, 2005 "May 2004" Title: Weather based technologies for residential irrigation scheduling: technical review report: prepared for Municipal Water District Year: 2004, 2005 "May 2004" Close