Colorado River Cutthroat Trout (O.C
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Arizona TIM PALMER FLICKR
Arizona TIM PALMER FLICKR Colorado River at Mile 50. Cover: Salt River. Letter from the President ivers are the great treasury of noted scientists and other experts reviewed the survey design, and biological diversity in the western state-specific experts reviewed the results for each state. RUnited States. As evidence mounts The result is a state-by-state list of more than 250 of the West’s that climate is changing even faster than we outstanding streams, some protected, some still vulnerable. The feared, it becomes essential that we create Great Rivers of the West is a new type of inventory to serve the sanctuaries on our best, most natural rivers modern needs of river conservation—a list that Western Rivers that will harbor viable populations of at-risk Conservancy can use to strategically inform its work. species—not only charismatic species like salmon, but a broad range of aquatic and This is one of 11 state chapters in the report. Also available are a terrestrial species. summary of the entire report, as well as the full report text. That is what we do at Western Rivers Conservancy. We buy land With the right tools in hand, Western Rivers Conservancy is to create sanctuaries along the most outstanding rivers in the West seizing once-in-a-lifetime opportunities to acquire and protect – places where fish, wildlife and people can flourish. precious streamside lands on some of America’s finest rivers. With a talented team in place, combining more than 150 years This is a time when investment in conservation can yield huge of land acquisition experience and offices in Oregon, Colorado, dividends for the future. -
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 .................................................................................................................................................................. -
Environmental Flows and Water Demands in Arizona
Environmental Flows and Water A University of Arizona Water Resources Research Center Project Demands in Arizona ater is an increasingly scarce resource and is essential for Arizona’s future. Figure 1. Elements of Environmental Flow WWith Arizona’s population growth and Occurring in Seasonal Hydrographs continued drought, citizens and water managers have been taking a closer look at water supplies in the state. Municipal, industrial, and agricul- tural water users are well-represented demand sectors, but water supplies and management to benefit the environment are not often consid- ered. This bulletin explains environmental water demands in Arizona and introduces information essential for considering environmental water demands in water management discussions. Considering water for the environment is impor- tant because humans have an interconnected and interdependent relationship with the envi- ronment. Nature provides us recreation oppor- tunities, economic benefits, and water supplies Data Source: to sustain our communities. USGS stream gage data Figure 2: Human Demand and Current Flow in Arizona Environmental water demands (or environmental flow) (circle size indicates relative amount of water) refers to how much water is needed in a watercourse to sustain a healthy ecosystem. Defining environmental water demand goes beyond the ecology and hydrol- Maximum ogy of a system and should include consideration for Flows how much water is required to achieve an agreed Industrial 40.8 maf Industrial SW Municipal upon level of river health, as determined by the GW 1% GW 8% water-using community. Arizona’s native ani- 4% mals and plants depend upon dynamic flows commonly described according to the natural Municipal SW flow regime. -
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. -
June 2021 Arizona Office of Tourism Monthly State Parks Visitation Report
June 2021 Arizona Office of Tourism Monthly State Parks Visitation Report Arizona State Park Visitation June June 2021 2020 YTD State Park % Chg 2021 2020 YTD YTD % Chg Alamo Lake SP 1,237 1,924 -35.7% 48,720 46,871 3.9% Buckskin Mountain SP 11,092 9,292 19.4% 49,439 45,627 8.4% Catalina SP 6,598 2,420 172.6% 154,763 156,234 -0.9% Cattail Cove SP 10,138 14,908 -32.0% 52,221 67,256 -22.4% Colorado River SHP 167 57 193.0% 2,589 6,220 -58.4% Dead Horse Ranch SP 17,142 18,748 -8.6% 126,799 120,044 5.6% Fool Hollow Lake RA 16,380 25,104 -34.8% 55,360 63,341 -12.6% Fort Verde SHP 706 521 35.5% 4,672 2,654 76.0% Granite Mountain Hotshots MSP 1,076 1,380 -22.0% 11,778 14,874 -20.8% Homolovi SP 4,032 1,982 103.4% 22,007 11,470 91.9% Jerome SHP 4,099 1,991 105.9% 21,789 14,109 54.4% Kartchner Caverns SP 7,776 2,045 280.2% 44,020 57,663 -23.7% Lake Havasu SP 66,040 74,493 -11.3% 241,845 337,920 -28.4% Lost Dutchman SP 4,198 3,651 15.0% 122,844 132,399 -7.2% Lyman Lake SP 11,169 10,625 5.1% 30,755 38,074 -19.2% McFarland SHP 166 0 1,213 2,942 -58.8% Oracle SP 270 486 -44.4% 6,994 9,191 -23.9% Patagonia Lake SP 25,058 30,706 -18.4% 118,311 126,873 -6.7% Picacho Peak SP 1,893 1,953 -3.1% 64,084 68,800 -6.9% Red Rock SP 12,963 6,118 111.9% 56,356 33,228 69.6% Riordan Mansion SHP 777 0 2,188 2,478 -11.7% River Island SP 2,623 3,004 -12.7% 18,089 19,411 -6.8% Roper Lake SP 8,049 12,394 -35.1% 52,924 49,738 6.4% Slide Rock SP 54,922 33,491 64.0% 231,551 110,781 109.0% Tombstone Courthouse SHP 2,875 1,465 96.2% 18,261 16,394 11.4% Tonto Natural Bridge SP 8,146 7,161 13.8% 54,950 36,557 50.3% Tubac Presidio SHP 261 117 123.1% 4,240 2,923 45.1% Yuma Territorial Prison SHP 2,206 1,061 107.9% 28,672 26,505 8.2% Total All Parks 282,059 267,097 5.6% 1,647,434 1,620,577 1.7% Note: Dankworth Pond SP data is included in Roper Lake SP, Sonoita Creek SNA is included in Patagonia Lake SP and Verde River Greenway SNA is included in Dead Horse Ranch SP. -
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. -
Appendix L—Acec Evaluations for the Price Resource Management Plan
Proposed RMP/Final EIS Appendix L APPENDIX L—ACEC EVALUATIONS FOR THE PRICE RESOURCE MANAGEMENT PLAN INTRODUCTION Section 202(c)(3) of the Federal Land Policy and Management Act (FLPMA) requires that priority be given to the designation and protection of areas of critical environmental concern (ACEC). FLPMA Section 103 (a) defines ACECs as public lands for which special management attention is required (when such areas are developed or used or when no development is required) to protect and prevent irreparable damage to important historic, cultural, or scenic values; fish and wildlife resources; or other natural systems or processes or to protect life and safety from natural hazards. CURRENTLY DESIGNATED ACECS BROUGHT FORWARD INTO THE PRICE RMP FROM THE SAN RAFAEL RMP In its Notice of Intent (NOI) to prepare this Resource Management Plan (RMP) (Federal Register, Volume 66, No. 216, November 7, 2001, Notice of Intent, Environmental Impact Statement, Price Resource Management Plan, Utah), BLM identified the 13 existing ACECs created in the San Rafael RMP of 1991. The NOI explained BLM’s intention to bring these ACECs forward into the Price Field Office (PFO) RMP. A scoping report was prepared in May 2002 to summarize the public and agency comments received in response to the NOI. The few comments that were received were supportive of continued management as ACECs. The ACEC Manual (BLM Manual 1613, September 29, 1988) states, “Normally, the relevance and importance of resource or hazards associated with an existing ACEC are reevaluated only when new information or changed circumstances or the results of monitoring establish a need.” The following discussion is a brief review of the existing ACECs created by the San Rafael RMP of 1991 and discussed in the Environmental Impact Statement (EIS). -
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). -
CRWAS Phase I Yampa River – Statemod Model Brief
CRWAS Phase I Yampa River – StateMod Model Brief 1. Introduction................................................................................................................................. 2 2. Model Components..................................................................................................................... 4 2.1 Inflow Hydrology.................................................................................................................4 2.1.1 Data Sources and Filling Techniques.........................................................................6 2.2 Physical Systems.................................................................................................................. 8 2.2.1 Data Sources and Filling Techniques.........................................................................9 2.3 Water Demands...................................................................................................................10 2.3.1 Data Sources and Filling Techniques...................................................................... 10 2.4 Legal and Administrative Conditions................................................................................ 11 2.4.1 Data Sources and Filling Techniques.......................................................................12 3. Model Calibration......................................................................................................................13 3.1 First Step Calibration..........................................................................................................13 -
GILA TROUT (Oncorhynchus Gilae)
(Technical Review Draft, April 2002) GILA TROUT (Oncorhynchus gilae) (Third Revision) RECOVERY PLAN (Original Approved: January 12, 1979) (First Revision Approved: January 3, 1984) (Second Revision Approved: December 8, 1993) Prepared by John Pittenger (Purchase Order 201819M251) for Region 2 U.S. Fish and Wildlife Service Albuquerque, New Mexico Approved: XXX Regional Director, U.S. Fish and Wildlife Service Date: DISCLAIMER Recovery plans delineate reasonable actions believed to be required to recover and/ or protect listed species. Plans published by the U.S. Fish and Wildlife Service or national Marine Fisheries Service are sometimes prepared with the assistance of recovery teams, contractors, State agencies, and other affected and interested parties. Recovery teams serve as independent advisors to the Services. Plans are reviewed by the public and submitted to additional peer review before they are adopted by the Services. Objectives of the plan will be attained and any necessary funds made available subject to budgetary and other constraints affecting the parties involved, as well as the need to address other priorities. Recovery plans do not obligate other parties to undertake specific tasks and may not represent the views nor the official positions or approval of any individuals or agencies involved in the plan formulation, other than the U.S. Fish and Wildlife Service/National Marine Fisheries Service. They represent the official position of the National Marine Fisheries Service/U.S. Fish and Wildlife Service only after they have been signed by the Assistant Administrator/Regional Director or Director as approved. Approved recovery plans are subject to modification as dictated by new findings, changes in species status, and the completion of recovery tasks.