Redband Trout Resilience and Challenge in a Changing Landscape
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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 .................................................................................................................................................................. -
Fish Stocking Plan
Draft Application for a New License Major Project – Existing Dam New Bullards Bar Reservoir Fish Stocking Plan Security Level: Public Yuba River Development Project FERC Project No. 2246 Draft – December 2013 ©2013, Yuba County Water Agency All Rights Reserved Yuba County Water Agency Yuba River Development Project FERC Project No. 2246 Table of Contents Section No. Description Page No. Glossary – Definitions of Terms, Acronyms and Abbreviations ........................................... GLO-1 1.0 Introduction ...................................................................................................................... 1-1 1.1 Background .......................................................................................................... 1-1 1.1.1 Yuba River Development Project ............................................................ 1-1 1.2 Purpose of the New Bullards Bar Reservoir Fish Stocking Plan ......................... 1-5 1.3 Objectives of the New Bullards Bar Reservoir Fish Stocking Plan..................... 1-5 1.4 Contents of the New Bullards Bar Reservoir Fish Stocking Plan ....................... 1-5 2.0 Regulatory Framework, Fish Assemblage, and Stocking History ................................... 2-1 2.1 Regulatory Framework for Fish Stocking in New Bullards Bar Reservoir ......... 2-1 2.1.1 Forest Service and Cal Fish and Wildlife – Memorandum of Understanding .......................................................................................... 2-1 2.1.2 California Fish and Wildlife Code .......................................................... -
Redband Trout Sub-Sp. (Oncorhynchus Mykiss Sub-Species) Data: Trout and Salmon of North America, Behnke, 2002; Various State and Federal Documents Partners: CA, OR
Redband Trout Sub-Sp. (Oncorhynchus mykiss sub-species) Data: Trout and Salmon of North America, Behnke, 2002; Various state and federal documents Partners: CA, OR. WA, NV, ID, MT, FS, FWS, BLM, Tribes__________________ Status of the Redband Trout: Various forms Historic Distribution of Redband Trout of the Redband trout (RBT) were petitioned to (modified from Behnke, 1996) be listed as Threatened or Endangered in the late 1990’s, but the U.S. Fish and Wildlife Service determined that the sub-species, in the various drainages, did not need the protection of the Endangered Species Act. The various forms of Redband trout in California, Oregon, Washington, Nevada, Idaho and Montana are considered to be sensitive species or species of concern in all the states. The BLM also considers several populations of Redband Trout to be a “sensitive Species”. Sportfishing Status of Redband trout: Native populations of redband trout provide diverse and popular recreational angling opportunities. Their willingness to take a variety of fishing gear, impressive fighting ability when hooked, spectacular appearance and potential to reach large size all contribute to their popularity. Special regulations for waters possessing redband trout population are Although the current distribution is not used to balance angling opportunities with accurately described, regionally located surveys conservation needs. For example, in Nevada, do give some good information. For the recreational angling is allowed for redband purposes of this status assessment, distribution trout with harvest and possession limits ranging in four geographic population groups is from five to ten trout. Angler use on these described. They include 1) the upper redband trout streams and rivers has averaged Sacramento River Basin; 2) The upper interior approximately 7,000 angler use days per year Great Basin in Oregon and Nevada; 3) the since 1993. -
Long-Term Captive Breeding Does Not Necessarily Prevent Reestablishment: Lessons Learned from Eagle Lake Rainbow Trout
Rev Fish Biol Fisheries DOI 10.1007/s11160-011-9230-x RESEARCH PAPER Long-term captive breeding does not necessarily prevent reestablishment: lessons learned from Eagle Lake rainbow trout Gerard Carmona-Catot • Peter B. Moyle • Rachel E. Simmons Received: 7 March 2011 / Accepted: 18 July 2011 Ó Springer Science+Business Media B.V. 2011 Abstract Captive breeding of animals is often cited recovering as habitat. With the exception of an as an important tool in conservation, especially for abundant alien brook trout (Salvelinus fontinalis) fishes, but there are few reports of long-term population in Pine Creek, the habitat factors that led (\50 years) success of captive breeding programs, to the presumed near-extinction of Eagle Lake rainbow even in salmonid fishes. Here we describe the captive trout in the early twentieth century have been amelio- breeding program for Eagle Lake rainbow trout, rated, although the final stages of reestablishment Oncorhynchus mykiss aquilarum, which is endemic (eradication of brook trout, unequivocal demonstration to the Eagle Lake watershed of northeastern Califor- of successful spawning migration) have still not been nia. The population in Eagle Lake has been dependent completed. The Eagle Lake rainbow trout story shows on captive breeding for more than 60 years and that long-term captive breeding of migratory salmonid supports a trophy fishery in the lake. Nevertheless, fishes does not necessarily prevent reestablishment of the basic life history, ecological, and genetic traits of wild populations, provided effort is made to counter the subspecies still seem to be mostly intact. Although the effects of hatchery selection and that natural management has apparently minimized negative habitats are restored for reintroduction. -
1 EAGLE LAKE RAINBOW TROUT Oncorhynchus Mykiss Aquilarum
EAGLE LAKE RAINBOW TROUT Oncorhynchus mykiss aquilarum (Snyder) Status: High Concern. The Eagle Lake rainbow trout (ELRT) does not exist as a self-sustaining wild population because of dependence on hatchery propagation. Habitat degradation and the presence of alien brook trout in Pine Creek, the ELRT’s principal spawning grounds, along with continued reliance on hatchery production to maintain the ELRT population will make it increasingly difficult to re-establish a wild population. Description: This subspecies is similar to other rainbow trout in gross morphology (see Moyle 2002), but differs slightly in meristic counts, especially in having finer scales than coastal rainbow trout. It is also distinctive in possessing 58 chromosomes, rather than the 60 typical of other rainbow trout (Busack et al. 1980). Taxonomic Relationships: Snyder (1917) described this trout as a subspecies of rainbow trout, Salmo gairdneri aquilarum. However, Hubbs and Miller (1948) examined Snyder's specimens and concluded that ELRT were derived from hybridization between native Lahontan cutthroat trout (presumed to have occupied Eagle Lake prehistorically) and introduced rainbow trout. Miller (1950) later retracted the hybridization theory. Needham and Gard (1959) then suggested that ELRT were descended from introduced or immigrant rainbow trout from the Feather or Pit River drainages. Behnke (1965, 1972) proposed a redband-rainbow hybrid origin, although redband trout are now considered to be rainbow trout subspecies. Busack et al. (1980), in an extensive electrophoretic, karyotypic and meristic analysis, suggested that ELRT were derived either from immigration or an unrecorded introduction of a rainbow trout with 58 chromosomes. The distinctive morphology, ecology, and physiology of this form all point to ELRT being derived from natural colonization from the Sacramento River drainage. -
Recreational Fishing in the Golden Trout Wilderness at $148,000 to $713,000 a Year
ECONOMIC VALUE OF GOLDEN TROUT FISHING IN THE GOLDEN TROUT WILDERNESS, CALIFORNIA An Analysis By Carolyn Alkire, Ph.D. Resource Economist A Report for California Trout March 21, 2003 ACKNOWLEDGEMENTS Thanks to the many individuals who provided essential data and information, without which this study would not have been possible: Del Hubbs, Adam McClory, and Julie Molzahn, Inyo National Forest; Cheryl Bauer and Judi Kaiser, Sequoia National Forest; Jim Shackelford, Forest Service Region 5; and Donn Burton and Dave Lentz, California Department of Fish and Game. The author is grateful for the professional review by Dr. John Loomis. Stan Stephens of the California Department of Fish and Game and Dr. Robert Richardson also offered helpful comments and suggestions. This report was expertly edited by Deanne Kloepfer. California Trout would like to thank Joseph Tomelleri for the use of his trout illustrations. California Trout thanks C. Pat Patterson and Bill Hooper for generously funding this report. Cover illustration courtesy of Michael Flynn FOREWORD By R. Brett Matzke Public Lands Director California Trout, Inc. Cattle began grazing the Kern Plateau more than 130 years ago, long before the area and surrounding environs were established as the Inyo and Sequoia national forests. Various studies have documented that cattle grazing can seriously damage water and land resources. But attempts to reform grazing management policy on the Kern Plateau and to protect native species in this case, California's state fish, the golden trout, and its close relative shave met with little success. In part, the failure to reform grazing management stems from the long-held view that cattle ranching is the cornerstone of the local economy. -
III. Eagle Lake Rainbow Trout/Tishes of Pine Creek and Eagle Lake
III. Eagle Lake Rainbow Trout/Tishes of Pine Creek and Eagle Lake It is from a storied prize catch that comes a secretive past: the Eagle Lake rainbow trout of disagreed upon origin is no longer naturally reproducing. History has been less than kind to the ELRT as actions of the past created potential extinction. Timely intervention and persistence in restoration efforts has brought the ELRT to a sort of crossroads today: hatchery production provides a quality fishing experience for visitors to Eagle Lake (and other waters in the western United States), while efforts to improve habitat has likely made spawning grounds accessible once again. The missing link at this point is whether the fish still have the capability to ascend Pine Creek at an opportune time to spawn and return (or for progeny to return) to complete their life cycle. All fish have been completely stopped by the dam in their upstream quest to migrate at the trapping and spawning facility near Spalding. From 1959 through 1994, ELRT were known to migrate past the dam during years of high flow when conditions allowed them to pass. Reconstructed in 1995 to more effectively prevent erosion and upstream movement of fish, it is highly unlikely that any ELRT have made it over the barrier. Questions arise as to the ability of these "hatchery" fish to know when to migrate, and where or how far upstream to go. Have we raised fish that are prograrnmed to spawn earlier now than in the past? If fish today are many generations removed from upstream migration, will they know how far to go, or know which stream or segment provides spawning gravels? Is it important to have these fish spawn naturally and occupy their "original" habitat? The CRMP group must continue to work on the answers to these questions. -
Hat-Warren1986 Ashton Hatchery Annual Report
Hatchery 07 Article 02 ASHTON HATCHERY ANNUAL REPORT October 1, 1985 to September 30, 1986 by Roland Warren Fish Hatchery Superintendent II October 1987 TABLE OF CONTENTS Page ABSTRACT .......................................................... 1 INTRODUCTION ...................................................... 2 OBJECTIVES ........................................................ 2 FISH PRODUCTION ................................................... 2 FISH RELEASES ..................................................... 3 FISH FEED UTILIZED ................................................ 4 FISH HEALTH ....................................................... 4 HATCHERY IMPROVEMENTS ............................................. 4 MISCELLANEOUS ACTIVITIES .......................................... 4 ACKNOWLEDGMENTS ................................................... 5 LIST OF TABLES Table 1. Eye eggs ........................................................2 Table 2. Fish transfers ..................................................3 Table 3. Fish planted from October 1, 1985 to September 30, 1986 ............................................................3 Table 4. Fish feed consumed at Ashton Hatchery from October 1, 1985 to September 30, 1986 ............................4 1 ABSTRACT During the 1985-86 fish year, Ashton Hatchery received 2,776,929 eyed eggs. Rainbow trout, Kamloops rainbow trout, brown trout, brook trout, cutthroat trout, golden trout, and grayling were the species hatched. A total of 46,407 lb of fish were produced at the -
Drought Assessments of Little Kern Golden Trout (Oncorhynchus Mykiss Whitei)
Drought assessments of Little Kern Golden Trout (Oncorhynchus mykiss whitei) 2015 Tulare County State of California Department of Fish and Wildlife Heritage and Wild Trout Program Prepared by Stephanie Hogan and Claire Buchanan Overview In 2013, the California Department of Fish and Wildlife (CDFW) Heritage and Wild Trout Program (HWTP) initiated drought assessments on several waters in California. The CDFW Threatened Trout Committee and HWTP staff developed a prioritized list of streams with native trout species of high conservation value that may be at risk due to drought conditions. This list was prioritized based on genetic integrity with a focus on putative populations, species on federal and/or state endangered species lists, and perceived threat level. The latter included consideration of slope, aspect, streamflow, water source, and surrounding land use activities. A structured decision-making matrix was created to aid staff in assessing drought conditions, evaluate whether fish rescues were necessary to protect certain populations and identify potential locations for translocations (within the same waterbody, within basin or out-of-basin; Table 1). Little Kern Golden Trout are listed as threatened under the Federal Endangered Species Act and drought monitoring locations were established in 2013 in five key tributaries to the Little Kern River. These streams were originally selected because they support populations with high genetic integrity and a severe fire burned this area in 2011. These sites were surveyed in 2014 and 2015 (Hogan et. al. 2014); this report summarizes the results of the 2015 drought assessments in Lion, Sheep, Tamarack, Willow, and No Name creeks. Need Negative effects from drought on inland native trout populations and their habitats have been historically documented and, in some cases, led to localized extirpation. -
Sympatric Relationship Between Redband Trout and Non-Native Brook Trout in the Southeastern Oregon Great Basin
Environ Biol Fish DOI 10.1007/s10641-013-0157-z Sympatric relationship between redband trout and non-native brook trout in the Southeastern Oregon Great Basin Stephanie A. Miller & Stephanie Gunckel & Steve Jacobs & Dana R. Warren Received: 17 May 2012 /Accepted: 18 July 2013 # Springer Science+Business Media Dordrecht 2013 Abstract Brook trout (Salvelinus fontinalis) and rain- between sympatric and allopatric locations that would bow trout (Oncorhynchus mykiss) have been widely indicate differentiation in site level habitat preferences introduced outside their respective ranges within North for each trout species. We found that sympatric loca- America causing declines and displacement of native tions had more wood but similar fish community struc- trout. Yet, successful coexistence of native and non- ture. Mean length and densities of redband trout were native trout has received little attention. Here we eval- higher at allopatric locations. However, in most years uated the effect of introduced brook trout on the size at sympatric locations total trout density was twice that and density of native redband trout in two invaded sub- of allopatric redband trout sites. Using comparable data basins in southeastern Oregon. In a multi-year study, from an eastern United States system where brook trout we investigated whether habitat and fish communities are native, sympatric sites had lower densities of brook differed between streams and stream reaches where trout; however, total trout density did not differ. We redband trout were allopatric versus where redband conclude that invading trout negatively impact native trout were sympatric with brook trout. We hypothe- trout densities; but in southeastern Oregon system the sized that redband trout would be less dense and have negative impact is minimized. -
Gold Can Still Be Found High in the Southern Sierra Nevada! The
California's Golden Treasure... Lake South America Sequoia-Kings Canyon National Park Our State Fish Sequoia & Inyo National Forests AW eek K E Cr - AH ce N lla Gold can still be found high in ER R Wa K IV ER y Cree k the southern Sierra Nevada! ne it Mount Whitney h W The fabulous "golden trout" SEQUOIA-KINGS CANYON Crabtree Lakes B i of this region is represented g Ar ro NATIONAL yo C ck Creek r Ro by two subspecies: the e e k PARK California golden trout and K E R N the Little Kern golden trout. k e The Kern River rainbow, a e k r e re C k Rattlesnake C R e t e Inyo Cr I u y V o r e E k T l close relative, is also native R u n e M d l o to the upper Kern River. G National r r e e r g g e n k n i reek g WILDERNESS C e i r le r e n if Coy Cr t t o i R te S k S r t r e t k e e h S a g r g e in i t r C P t R f S Kern Lake e n is k r ew The exceptional c L L e Dry a R aw C r ou K tr be re S k gh Cre S rr ek o a e ek y d m e C a a r TROUT re T ek S C k p Creek e Kern Peak w Kern Lake e r i o r k beauty and brilliant n l l Creek C i ure k e g S or e Forest W e F w r C ll e GOLDEN e o C r r H d Olancha Peak e gget Le t Creek C a k e k ee e c k r M o C on d R color of golden trout i l L o Alpine C d e C r R r e k e g e e L d in e k D l r r t k I o e C e S e T M e ou C n r g led to their designation n p a C t T a n e in C h S k o e e C g c e e L n a r L o n r C r ine Mi o o e N le L d E C M e re a ek k C KE r as our State fish in 1947, R eek k N Cree S s u k m c i l ek m C re R C o i u t sh n i d r C and is one of the primary F e M g r o in e L R u r n t e l t S k o I ain y V d H M E o e R reasons for the creation of n a d e o y w b s e e C Sequoia C r r e e e SOUTH e the Golden Trout Wilderness. -
Microsoft Outlook
Joey Steil From: Leslie Jordan <[email protected]> Sent: Tuesday, September 25, 2018 1:13 PM To: Angela Ruberto Subject: Potential Environmental Beneficial Users of Surface Water in Your GSA Attachments: Paso Basin - County of San Luis Obispo Groundwater Sustainabilit_detail.xls; Field_Descriptions.xlsx; Freshwater_Species_Data_Sources.xls; FW_Paper_PLOSONE.pdf; FW_Paper_PLOSONE_S1.pdf; FW_Paper_PLOSONE_S2.pdf; FW_Paper_PLOSONE_S3.pdf; FW_Paper_PLOSONE_S4.pdf CALIFORNIA WATER | GROUNDWATER To: GSAs We write to provide a starting point for addressing environmental beneficial users of surface water, as required under the Sustainable Groundwater Management Act (SGMA). SGMA seeks to achieve sustainability, which is defined as the absence of several undesirable results, including “depletions of interconnected surface water that have significant and unreasonable adverse impacts on beneficial users of surface water” (Water Code §10721). The Nature Conservancy (TNC) is a science-based, nonprofit organization with a mission to conserve the lands and waters on which all life depends. Like humans, plants and animals often rely on groundwater for survival, which is why TNC helped develop, and is now helping to implement, SGMA. Earlier this year, we launched the Groundwater Resource Hub, which is an online resource intended to help make it easier and cheaper to address environmental requirements under SGMA. As a first step in addressing when depletions might have an adverse impact, The Nature Conservancy recommends identifying the beneficial users of surface water, which include environmental users. This is a critical step, as it is impossible to define “significant and unreasonable adverse impacts” without knowing what is being impacted. To make this easy, we are providing this letter and the accompanying documents as the best available science on the freshwater species within the boundary of your groundwater sustainability agency (GSA).