RULES and REGULATIONS the Lahontan Cutthroat Trout (Salmo
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Center Comments to the California Department of Fish and Game
July 24, 2006 Ryan Broderick, Director California Department of Fish and Game 1416 Ninth Street, 12th Floor Sacramento, CA 95814 RE: Improving efficiency of California’s fish hatchery system Dear Director Broderick: On behalf of the Pacific Rivers Council and Center for Biological Diversity, we are writing to express our concerns about the state’s fish hatchery and stocking system and to recommend needed changes that will ensure that the system does not negatively impact California’s native biological diversity. This letter is an update to our letter of August 31, 2005. With this letter, we are enclosing many of the scientific studies we relied on in developing this letter. Fish hatcheries and the stocking of fish into lakes and streams cause numerous measurable, significant environmental effects on California ecosystems. Based on these impacts, numerous policy changes are needed to ensure that the Department of Fish and Game’s (“DFG”) operation of the state’s hatchery and stocking program do not adversely affect California’s environment. Further, as currently operated, the state’s hatchery and stocking program do not comply with the California Environmental Quality Act, Administrative Procedures Act, California Endangered Species Act, and federal Endangered Species Act. The impacts to California’s environment, and needed policy changes to bring the state’s hatchery and stocking program into compliance with applicable state and federal laws, are described below. I. FISH STOCKING NEGATIVELY IMPACTS CALIFORNIA’S NATIVE SALMONIDS, INCLUDING THREATENED AND ENDANGERED SPECIES Introduced salmonids negatively impact native salmonids in a variety of ways. Moyle, et. al. (1996) notes that “Introduction of non-native fish species has also been the single biggest factor associated with fish declines in the Sierra Nevada.” Moyle also notes that introduced species are contributing to the decline of 18 species of native Sierra Nevada fish species, and are a major factor in the decline of eight of those species. -
Bonneville Cutthroat Trout (Oncorhynchus Clarki Utah) Bonneville Cutthroat Trout Is One of Three Cutthroat Trout Subspecies Native to Utah
FISH Bonneville Cutthroat Trout (Oncorhynchus clarki utah) Bonneville cutthroat trout is one of three cutthroat trout subspecies native to Utah. Bonneville cutthroat trout historically occurred in the Pleistocene Lake Bonneville basin, which included portions of Idaho, Nevada, Utah, and Wyoming (Kershner 1995). The desiccation of Lake Bonneville into the smaller Great Salt Lake and fragmentation of other stream and lake habitats may have led to three slightly differentiated groups of Bonneville cutthroat trout. These groups are found in the Bonneville basin proper, the Bear River drainage, and the Snake Valley (Behnke 1992). There are five known populations of pure strain Bonneville cutthroat trout on the Fishlake National Forest inhabiting approximately 38 miles of stream habitat. There are several recently reintroduced populations, and several small potential remnant populations. Habitat for the Bonneville cutthroat trout is widely distributed and variable. It ranges from high elevation (3,500 m mean sea level) streams with coniferous and deciduous riparian trees to low elevation (1,000 m mean sea level) streams in sage-steppe grasslands containing herbaceous riparian zones. As such, Bonneville cutthroat trout have adapted to a broad spectrum of habitat conditions throughout their range (Kershner 1995). Sexual maturity is typically reached during the second year for males and the third year for females (May et al. 1978). Both the age at maturity and the annual timing of spawning vary geographically with elevation, temperature, and life history strategy. Lake resident trout may begin spawning at two years of age and usually continue throughout their lives, while adfluvial individuals may not spawn for several years. -
The Native Trouts of the Genus Salmo of Western North America
CItiEt'SW XHPYTD: RSOTLAITYWUAS 4 Monograph of ha, TEMPI, AZ The Native Trouts of the Genus Salmo Of Western North America Robert J. Behnke "9! August 1979 z 141, ' 4,W \ " • ,1■\t 1,es. • . • • This_report was funded by USDA, Forest Service Fish and Wildlife Service , Bureau of Land Management FORE WARD This monograph was prepared by Dr. Robert J. Behnke under contract funded by the U.S. Fish and Wildlife Service, the Bureau of Land Management, and the U.S. Forest Service. Region 2 of the Forest Service was assigned the lead in coordinating this effort for the Forest Service. Each agency assumed the responsibility for reproducing and distributing the monograph according to their needs. Appreciation is extended to the Bureau of Land Management, Denver Service Center, for assistance in publication. Mr. Richard Moore, Region 2, served as Forest Service Coordinator. Inquiries about this publication should be directed to the Regional Forester, 11177 West 8th Avenue, P.O. Box 25127, Lakewood, Colorado 80225. Rocky Mountain Region September, 1980 Inquiries about this publication should be directed to the Regional Forester, 11177 West 8th Avenue, P.O. Box 25127, Lakewood, Colorado 80225. it TABLE OF CONTENTS Page Preface ..................................................................................................................................................................... Introduction .................................................................................................................................................................. -
Biology and Management of Threatened and Endangered Western Trouts
Biology and Management of Threatened and Endangered Western Trouts August 1976 USDA Forest Service General Technical Report RM-28 Rocky Mountain Forest and Range Experiment Station Forest Service U.S. Department of Agriculture Fort Collins, Colorado 80521 Abstract Behnke, R. J., and Mark Zarn. 1976. Biology and management of threatened and endangered western trouts. USDA For. Sew. Gen. Tech. Rep. RM-28, 45 p. Rocky Mt. For. and Range Exp. Stn., Fort Collins, Colo. Discusses taxonomy, reasons for decline, life history and ecology, and sug- gestions for preservation and management of six closely related trouts native to western North America: Colorado River cutthroat, Salmo clarki pleuriticus; green- back trout, S. c. stomias; Lahontan cutthroat, S. c. henshawi; Paiute trout, S. c. seleniris; Gila trout, S. gilae; and Arizona native trout, S. apache. Meristic characters, distribution and status, habitat requirements and limiting factors, protective measures, and management recommendations are presented for each taxon. Keywords: Native trout, Salrno clarki pleuriticus. Sali?zo ckurki stoi~zius. Sulnzo clarki herzshawi, Salmo clarki seleniris, Salrno gilue. Sulrno uprrchc. USDA Forest Service General Technical Report RM-28 August 1976 Biology and Management of Threatened and Endangered Western Trouts R. J. Behnke Colorado State University Mark Zarn Conservation Library Denver Public Library Information reported here was prepared under contract by the Conservation Library of the Denver Public Library, through the Rocky Mountain Forest and Range Experiment Station. The report is printed as prepared by the authors; opinions are not necessarily those of the U.S. Forest Service. TABLE OF CONTENTS I . GJ3NERAL MANAGEMENT GUIDELINES FOR RAE3 AND ENDANGJIRED WESTERN TROUTS Introduction .......................... -
History of Lahontan Cutthroat Trout in Spring Creek, Utah
Spring Creek Population History of the Pyramid Lake Rediscovery (Again) Unfortunately, given its small size, the trout Lahontan Cutthroat population at Spring Creek has a very low In October 2009, a team from Weber State probability of survival. It lacks the numbers The Lahontan cutthroat trout, Oncorhynchus University in conjunction with personnel and space necessary to maintain sufficient clarkii henshawi, is native to the Lahontan Basin from the DWR identified several specimens genetic diversity. It is believed that for a on the border between California and Nevada. believed to be of a pure or hybrid strain of mountain stream cutthroat population to For thousands of years it thrived and played the Pyramid Lake Lahontan cutthroat trout survive it must have a minimum of 3.3 km an important economic and cultural role in Spring Creek in Uintah, Utah. Using of habitat and an abundance in the area of among the Native American tribes of the electrofishers and dip nets, a 600 m stretch 0.3 fish per meter.3 Based on our region. The largest strain of this fish of the stream was sampled. A maximum observations, the Spring Creek population originated in Pyramid Lake, in western of 16 different individuals was collected in A Unique Environment has a maximum abundance of 0.1 fish/m Nevada and has reached recorded weights of two sampling trips. The fish appeared to Spring Creek’s unique vegetation and only 200 m of habitat. However, against up to 41 pounds, making it the largest “The Fish that Won’t Die” be restricted to a 200 m stretch. -
Colorado River Cutthroat Trout (Oncorhynchus Clarkii Pleuriticus): a Technical Conservation Assessment
Colorado River Cutthroat Trout (Oncorhynchus clarkii pleuriticus): A Technical Conservation Assessment Prepared for the USDA Forest Service, Rocky Mountain Region, Species Conservation Project October 10, 2008 Michael K. Young, Ph.D USDA Forest Service, Rocky Mountain Research Station 800 East Beckwith Avenue Missoula, Montana 59801 Peer Review Administered by American Fisheries Society 1 Young, M.K. (2008, October 10). Colorado River Cutthroat Trout (Oncorhynchus clarkii pleuriticus): a technical conservation assessment. [Online]. USDA Forest Service, Rocky Mountain Region. Available: http://www.fs.fed.us/r2/projects/scp/assessments/coloradorivercutthroattrout.pdf [date of access]. ACKNOWLEDGMENTS I thank Todd Allison, Warren Colyer, Greg Eaglin, Noah Greenwald, Paula Guenther-Gloss, Christine Hirsch, Jessica Metcalf, Dirk Miller, Kevin Rogers, and Dennis Shiozawa for their comments on an earlier version of this manuscript. My thanks also to Claire McGrath, Bruce Rosenlund, and Dave Winters for their reviews of a similar manuscript on a related subspecies. I appreciate the assistance of Dennis Shiozawa, Brigham Young University; Bill Wengert, Wyoming Game and Fish Department; and Dan Brauch, Colorado Division of Wildlife, for sharing a number of unpublished reports. This work was funded by the Species Conservation Project for Region 2 and the Rocky Mountain Research Station, both part of the USDA Forest Service. AUTHOR’S BIOGRAPHY Michael Young has been a Research Fisheries Biologist with the USDA Forest Service Rocky Mountain Research Station since 1989. His work focuses on the ecology and conservation of native coldwater fishes and the effects of natural and anthropogenic disturbances on stream ecosystems. COVER ILLUSTRATION CREDIT Illustration of the Colorado River Cutthroat Trout (Oncorhynchus clarkii pleuriticus) by © Joseph Tomelleri. -
Species Fact Sheet Coastal Cutthroat Trout Oncorhynchus Clarkii
Species Fact Sheet Coastal Cutthroat Trout Oncorhynchus clarkii STATUS: SPECIES OF The Southwestern Washington/Lower Columbia CONCERN River Distinct Population Southwestern Segment of Coastal cutthroat Washington/Lower trout potentially occurs in these Washington counties: Thurston, Columbia River Distinct Lewis, Yakima, Mason, Pacific, Population Segment Grays Harbor, Wahkiakum, Cowlitz, Clark, Skaminia, Klickitat, (Map may reflect historical as well as recent sightings) In 1999, the southwestern Washington/lower Columbia River Distinct Population Segment of coastal cutthroat trout, Oncorhynchus clarkii clarkii, was listed as threatened by National Marine Fisheries Service and the U.S. Fish and Wildlife Service FR 64(64): 16397-414. Subsequently, the Fish and Wildlife Service assumed sole regulatory jurisdiction. Based on changes in forest management regulation, the latest information indicating better than expected total populations in a large portion of the area, and an improved understanding of the ability of freshwater forms to produce anadromous progeny, the Fish and Wildlife Service withdrew the listing proposal in 2002. Current and Historical Status This Distinct Population Segment (DPS) includes populations in the Columbia River and its tributaries downstream from the Klickitat River in Washington and Fifteenmile Creek in Oregon to the Columbia River estuary; and the Willamette River and its tributaries downstream from Willamette Falls, to its confluence with the Columbia River, as well as in tributaries of Gray's Harbor and Willapa Bay. The southwestern Washington-lower Columbia River region historically supported highly productive coastal cutthroat trout populations. Coastal cutthroat trout are well distributed in most river basins in this geographic region, although probably in lower numbers relative to historical population sizes. -
Coyote Lake Lahontan Cutthroat Trout
Oregon Native Fish Status Report – Volume II Coyote Lake Lahontan Cutthroat Trout Existing Populations Lahontan cutthroat trout populations in the Coyote Lakes basin are remnant of a larger population inhabiting pluvial Lake Lahontan during the Pleistocene era. Hydrologic access routes of founding cutthroat trout from Lake Lahontan basin into the Coyote Lakes basin have yet to be described (Coffin and Cowan 1995). The Coyote Lake Lahontan Cutthroat Trout SMU is comprised of five populations (Table 1). All populations express a resident life history strategy; however large individuals in the Willow and Whitehorse Complex populations suggest a migratory component may exist. Table 1. Populations, existence status, and life history of the Coyote Lake Lahontan Cutthroat Trout SMU. Exist Population Description Life History Yes Willow Willow Creek and tributaries. Resident / Migratory Yes Whitehorse Complex Whitehorse and Little Whitehorse Creeks, and Resident / Migratory tributaries. Yes Doolittle Doolittle Creek above barrier. Resident Yes Cottonwood Cottonwood Creek above barrier. Resident Yes Antelope Antelope Creek. Resident Lahontan cutthroat trout from Willow and Whitehorse creeks were transplanted into Cottonwood Creek in 1971 and 1980, and into Antelope Creek in 1972 (Hanson et al. 1993). Whether Lahontan cutthroat trout were present in these creeks prior to stocking activities is disputed (Behnke 1992, Hanson et al. 1993, Coffin and Cowan 1995, K. Jones, ODFW Research Biologist, Corvallis, OR personal communication). For the purpose of this review these populations are considered native. Lahontan cutthroat trout were also transplanted into Fifteenmile Creek above a natural barrier (Hanson et al. 1993), but they did not establish a self- sustaining population (ODFW Aquatic Inventory Project, unpublished data). -
Market-Sized Cutthroat Trout Technical Report Western Regional Aquaculture Center
Feeds for Production of Market-sized Cutthroat Trout Technical Report WESTERN REGIONAL AQUACULTURE CENTER Gary Fornshell, University of Idaho Christopher Myrick, Colorado State University Madison Powell, University of Idaho Wendy Sealey, United States Fish and Wildlife Service United States Department of Agriculture National Institute of Food and Agriculture 1 PROJECT PARTICIPANTS Christopher Myrick, Colorado State University Cheyenne Owens, Colorado State University Biswamitra Patro, University of Idaho Madison Powell, University of Idaho Pat Blaufuss, University of Idaho Tracy Kennedy, University of Idaho Wendy Sealey, United States Fish and Wildlife Service Brian Ham, United States Fish and Wildlife Service Gary Fornshell, University of Idaho Jeremy Liley, Liley Fisheries, Inc. David Brock, Rangen, Inc. Jackie Zimmerman, Skretting USA Rick Barrows, Aquatic Feed Technologies, LLC Photo credits: Cover: Gary Fornshell Above: iStock.com/KaraGrubis 2 Table of Contents Introduction: Why Consider Cutthroat Trout? 1 Snake River Cutthroat Trout—A Culturable Cutthroat 2 Is Raising Fish for the Recreational Market Worthwhile? 3 Overcoming Challenges to Raising Cutthroat Trout 3 Fish Nutrition 101—A Primer on Feed Formulation 3 Feed Pellet Texture Matters 5 Cutthroat Trout Growth—Does It Match Rainbow Trout? 5 Thermal Growth Coefficient 5 Comparing Rainbow and Cutthroat Trout Performance 6 Suggested Readings 10 Acknowledgments 11 Figures 1. Snake River cutthroat trout. 1 2. Map showing the distribution of extant cutthroat trout 2 subspecies in the western United States. 3. Juvenile Snake River cutthroat trout ready for stocking. 3 4. Classic bell-shaped growth-temperature curve. 6 5. Sigmoid growth curve. Based on Fish Hatchery Management, Second Edition, Gary Wedemeyer, editor 7 6. -
Spatial Variation in Spawning Habitat of Cutthroat Trout in a Sediment
Transactions of the American Fisheries Society 125:768-779. 1996 © Copyright by the American Fisheries Society 1996 Spatial Variatio Spawninn i g Habita f Cutthroato t Troua n ti Sediment-Rich Stream Basin JAMES P. MAGEE' AND THOMAS E. McMAHON2 Biology Department, FishWildlifeand Program Montana State University, Bozeman, Montana 59717,USA RUSSELL E THUROW U.S. Forest Service, Intermountain Research Station 316 East Myrtle Street. Boise, Idaho 83702,USA Abstract.—We examined distributio habitad nan t characteristic f spawnino s g site f cutthroaso t trout Oncorhynchus clarki t varioua s spatial scale asseso st s effect f sedimentatioso n withi nlarga e basin in Montana. Redd density varied widely across the basin; nearly all (99%) of the 362 redds observed occurred in two high-elevation headwater tributaries. Redd density at the reach scale s positivelwa y correlate 0.001= 0.72= 2 P ,d(r ) with abundanc f spawnino e g gravels. Other habitat variables, such as gradient, width, depth, embeddedness, bank stability, and percent riffle, were not significantly correlated to redd density. Taylor Fork redds contained some of the highest proportions of fine sediments (<6.35 mm, mean = 41.6%; <0.85 mm, 17.9%) observed in egg pocket salmonif so d Rocke reddth n si y Mountain region. Cache Creek highl,a y disturbed subbasin, d significantlha y greater proportion f fino s e sediments smaller tha reddn i n 0.8m s m 5tha e nth undisturbed Wapiti Creek subbasin. High fine-sediment level vero reddestimaten t w i s d ylo sle d embryo survival (mean, 8.5%) t sedimentatiobu , t appeano limid o t r di n t recruitment r datOu a. -
Influence of Water Temperature and Beaver Ponds on Lahontan Cutthroat Trout in a High-Desert Stream, Southeastern Oregon
AN ABSTRACT OF THE THESIS OF Andrew G. Talabere for the degree of Master of Science in Fisheries Science presented on November 21. 2002. Title: Influence of Water Temperature and Beaver Ponds on Lahontan Cutthroat Trout in a High-Desert Stream, Southeastern Oregon Abstract approved Redacted for Privacy Redacted for Privacy The distribution of Lahontan cutthroat trout Oncorhynchus clarki henshawi was assessed in a high-desert stream in southeastern Oregon where beaver Castor canadensis are abundant. Longitudinal patterns of beaver ponds, habitat, temperature, and Lahontan cutthroat trout age group distribution were identified throughout Willow Creek. Three distinct stream segments were classified based on geomorphological characteristics. Four beaver-pond and four free-flowing sample sections were randomly located in each of the three stream segments. Beavers substantially altered the physical habitat of Willow Creek increasing the depth and width of available habitat. In contrast, there was no measurable effect on water temperature. The total number of Lahontan cutthroat trout per meter was significantly higher in beaver ponds than free-flowing sections. Although density (fish! m2) showed no statistically significant (P < 0.05) increase, values in beaver pondswere two-fold those of free-flowing sections. Age- 1 and young-of-the-year trout were absent or in very low numbers in lower Willow Creek because of elevated temperatures, but high numbers of age-2 and 3 (adults) Lahontan cutthroat trout were found in beaver ponds where water temperatures reached lethal levels (>24°C). Apparently survival is greater in beaver ponds than free-flowing sections as temperatures approach lethal limits. Influence of Water Temperature and Beaver Ponds on Lahontan Cutthroat Trout in a High- Desert Stream, Southeastern Oregon by Andrew G. -
Westslope Cutthroat Trout
Oregon Native Fish Status Report – Volume II Westslope Cutthroat Trout Existing Populations Oregon populations of westslope cutthroat trout are disjunct from their greater contiguous distribution in the Upper Missouri and Columbia basins of Montana and Idaho (Behnke 1992). The Westslope Cutthroat Trout SMU is comprised of 17 populations in the upper mainstem John Day River basin (Table 1). Populations were identified according to those defined in the interagency westslope cutthroat trout range-wide assessment (Shepard et al. 2003). The interagency assessment identified westslope cutthroat trout in Laycock Creek and the Upper John Day Complex as a single population. This review considers trout in Laycock Creek as a separate population from the Upper John Day Complex due to the significant distance between the two creeks. Most populations express a resident life history strategy, although, migratory forms exist in the Upper John Day Complex and possibly in the Canyon Complex (Hemmingsen 1999a, Shepard et al. 2003). Table 1. Populations, existence status, and life history of the John Day Westslope Cutthroat Trout SMU. Exist Population Description Life History Yes Upper John Day Includes upper mainstem river and tributaries. Resident / Migratory Complex Yes Strawberry Strawberry, Slide, and Squaw Creeks. Resident Yes Dixie Dixie and Standard Creeks. Resident Yes Indian Indian, Little Indian, and Overholt Creeks. Resident Yes Bear Bear Creek. Resident Yes Pine Pine Creek. Resident Yes Dog Dog Creek. Resident Yes Little Pine Little Pine Creek. Resident Yes Canyon Complex Includes Berry, Crazy, and Canyon creeks and Resident / migratory tributaries. Yes Laycock Laycock Creek. Yes Ingle Ingle Creek. Resident Yes Beech Upper Beech, Bear, Cottonwood, and Lake creeks.