Plains Minnow,Hybognathus Placitus
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Notropis Girardi) and Peppered Chub (Macrhybopsis Tetranema)
Arkansas River Shiner and Peppered Chub SSA, October 2018 Species Status Assessment Report for the Arkansas River Shiner (Notropis girardi) and Peppered Chub (Macrhybopsis tetranema) Arkansas River shiner (bottom left) and peppered chub (top right - two fish) (Photo credit U.S. Fish and Wildlife Service) Arkansas River Shiner and Peppered Chub SSA, October 2018 Version 1.0a October 2018 U.S. Fish and Wildlife Service Region 2 Albuquerque, NM This document was prepared by Angela Anders, Jennifer Smith-Castro, Peter Burck (U.S. Fish and Wildlife Service (USFWS) – Southwest Regional Office) Robert Allen, Debra Bills, Omar Bocanegra, Sean Edwards, Valerie Morgan (USFWS –Arlington, Texas Field Office), Ken Collins, Patricia Echo-Hawk, Daniel Fenner, Jonathan Fisher, Laurence Levesque, Jonna Polk (USFWS – Oklahoma Field Office), Stephen Davenport (USFWS – New Mexico Fish and Wildlife Conservation Office), Mark Horner, Susan Millsap (USFWS – New Mexico Field Office), Jonathan JaKa (USFWS – Headquarters), Jason Luginbill, and Vernon Tabor (Kansas Field Office). Suggested reference: U.S. Fish and Wildlife Service. 2018. Species status assessment report for the Arkansas River shiner (Notropis girardi) and peppered chub (Macrhybopsis tetranema), version 1.0, with appendices. October 2018. Albuquerque, NM. 172 pp. Arkansas River Shiner and Peppered Chub SSA, October 2018 EXECUTIVE SUMMARY ES.1 INTRODUCTION (CHAPTER 1) The Arkansas River shiner (Notropis girardi) and peppered chub (Macrhybopsis tetranema) are restricted primarily to the contiguous river segments of the South Canadian River basin spanning eastern New Mexico downstream to eastern Oklahoma (although the peppered chub is less widespread). Both species have experienced substantial declines in distribution and abundance due to habitat destruction and modification from stream dewatering or depletion from diversion of surface water and groundwater pumping, construction of impoundments, and water quality degradation. -
Plains Minnow
Plains Minnow - Hybognathus placitus Abundance: Rare Status: NSS3 (Bb) NatureServe: G4 S3 Population Status: Some populations appear vulnerable where they occur in low abundance and are restricted from historical distribution. This species has been extirpated from the North Platte River basin and may also be gone from the Bighorn River basin. Other populations appear stable. Limiting Factor: Habitat: impoundments in major river drainages reduced population size and distribution presumably through loss of stream connectivity, reduced turbidity, altered temperature regimes, and flow regulation. Comment: NSS Ranks are reviewed and revised with each SWAP revision. No changes were made for this species in this revision. Introduction Historically, the distribution of the plains minnow was similar to the range of the western silvery minnow (Hybognathus argyritis), found in the Missouri River and middle Mississippi River drainages, but was more widespread in western tributaries of the Missouri river (Pflieger 1997). They are considered native to the Mississippi, Red, Arkansas, and Missouri River drainages and are found primarily from Montana and Wyoming east to Iowa (Weitzel 2002). In Wyoming, plains minnow have been reported in the Belle Fourche, Big Horn, Cheyenne, Little Missouri, and Powder river drainages (northeastern and northwestern Missouri aquatic habitats; Baxter and Stone 1995; Patton 1997; McGree et al. 2010). They are rare in some drainages, for example, McGree et al. (2010) caught two above Keyhole Reservoir, Patton (1997) found one above and one below Keyhole Reservoir, and Pindel (1997) reported one from near Devils Tower. Dooenbos also (1998) captured low numbers in South Dakota near the state line. No Hybognathus sp. -
Western Silvery Minnow Hybognathus Argyritis
COSEWIC Assessment and Update Status Report on the Western Silvery Minnow Hybognathus argyritis in Canada ENDANGERED 2008 COSEWIC status reports are working documents used in assigning the status of wildlife species suspected of being at risk. This report may be cited as follows: COSEWIC. 2008. COSEWIC assessment and update status report on the western silvery minnow Hybognathus argyritis in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. vii + 38 pp. (www.sararegistry.gc.ca/status/status_e.cfm). Previous report: COSEWIC. 2001. COSEWIC assessment and update status report on the western silvery minnow Hybognathus argyritis in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. vii + 14 pp. (www.sararegistry.gc.ca/status/status_e.cfm) Houston, J.J.P. 1997. COSEWIC status report on the western silvery minnow Hybognathus argyritis in Canada. Committee on the Status of Endangered Wildlife in Canada. Ottawa. 14 pp. Production note: COSEWIC would like to acknowledge M.K. Lowdon, D.A. Watkinson, and W.G. Franzin for writing the update status report on the western silvery minnow, Hybognathus argyritis in Canada, prepared under contract with Environment Canada, overseen and edited by R. Campbell and C. Renaud, COSEWIC Freshwater Fishes Specialist Subcommittee Co-Chairs. For additional copies contact: COSEWIC Secretariat c/o Canadian Wildlife Service Environment Canada Ottawa, ON K1A 0H3 Tel.: 819-953-3215 Fax: 819-994-3684 E-mail: COSEWIC/[email protected] http://www.cosewic.gc.ca Également disponible en français sous le titre Ếvaluation et Rapport de situation du COSEPAC sur le méné d’argent de l’Ouest (Hybognathus argyritis) au Canada. -
Options for Selectively Controlling Non-Indigenous Fish in the Upper Colorado River Basin
Options for Selectively Controlling Non-Indigenous Fish in the Upper Colorado River Basin Draft Report June 1995 Leo D. Lentsch Native Fish and Herptile Coordinator Utah Division of Wildlife Resources Robert Muth Larval Fish Lab Colorado State University Paul D. Thompson Native Fish Biologist Utah Division of Wildlife Resources Dr. Todd A. Crowl Utah State University and Brian G. Hoskins Native Fish Technician Utah Division of Wildlife Resources Utah Division of Wildlife Resources Colorado River Fishery Project Salt Lake City, Utah TABLE OP CONTENTS PAGE ABSTRACT .......................... INTRODUCTION ...................... Non-Indigenous Problems ..... Objectives ................... Control Options ............. Mechanical Control ..... Chemical Control ....... Biological Control ..... Physicochemical Control METHODS .......................................................... Literature Review .......................................... Species Accounts ........................................... RESULTS .......................................................... Species Accounts ........................................... Clupeidae-Herrings ................................... Threadfin Shad .................................. Cyprinidae-Carps and Minnows ........................ Red Shiner ...................................... Common Carp ..................................... Utah Chub ........................................ Leathers ide Chub ................................ Brassy Minnow ................................... Plains Minnow -
Endangered Species
FEATURE: ENDANGERED SPECIES Conservation Status of Imperiled North American Freshwater and Diadromous Fishes ABSTRACT: This is the third compilation of imperiled (i.e., endangered, threatened, vulnerable) plus extinct freshwater and diadromous fishes of North America prepared by the American Fisheries Society’s Endangered Species Committee. Since the last revision in 1989, imperilment of inland fishes has increased substantially. This list includes 700 extant taxa representing 133 genera and 36 families, a 92% increase over the 364 listed in 1989. The increase reflects the addition of distinct populations, previously non-imperiled fishes, and recently described or discovered taxa. Approximately 39% of described fish species of the continent are imperiled. There are 230 vulnerable, 190 threatened, and 280 endangered extant taxa, and 61 taxa presumed extinct or extirpated from nature. Of those that were imperiled in 1989, most (89%) are the same or worse in conservation status; only 6% have improved in status, and 5% were delisted for various reasons. Habitat degradation and nonindigenous species are the main threats to at-risk fishes, many of which are restricted to small ranges. Documenting the diversity and status of rare fishes is a critical step in identifying and implementing appropriate actions necessary for their protection and management. Howard L. Jelks, Frank McCormick, Stephen J. Walsh, Joseph S. Nelson, Noel M. Burkhead, Steven P. Platania, Salvador Contreras-Balderas, Brady A. Porter, Edmundo Díaz-Pardo, Claude B. Renaud, Dean A. Hendrickson, Juan Jacobo Schmitter-Soto, John Lyons, Eric B. Taylor, and Nicholas E. Mandrak, Melvin L. Warren, Jr. Jelks, Walsh, and Burkhead are research McCormick is a biologist with the biologists with the U.S. -
Aquatic Fish Report
Aquatic Fish Report Acipenser fulvescens Lake St urgeon Class: Actinopterygii Order: Acipenseriformes Family: Acipenseridae Priority Score: 27 out of 100 Population Trend: Unknown Gobal Rank: G3G4 — Vulnerable (uncertain rank) State Rank: S2 — Imperiled in Arkansas Distribution Occurrence Records Ecoregions where the species occurs: Ozark Highlands Boston Mountains Ouachita Mountains Arkansas Valley South Central Plains Mississippi Alluvial Plain Mississippi Valley Loess Plains Acipenser fulvescens Lake Sturgeon 362 Aquatic Fish Report Ecobasins Mississippi River Alluvial Plain - Arkansas River Mississippi River Alluvial Plain - St. Francis River Mississippi River Alluvial Plain - White River Mississippi River Alluvial Plain (Lake Chicot) - Mississippi River Habitats Weight Natural Littoral: - Large Suitable Natural Pool: - Medium - Large Optimal Natural Shoal: - Medium - Large Obligate Problems Faced Threat: Biological alteration Source: Commercial harvest Threat: Biological alteration Source: Exotic species Threat: Biological alteration Source: Incidental take Threat: Habitat destruction Source: Channel alteration Threat: Hydrological alteration Source: Dam Data Gaps/Research Needs Continue to track incidental catches. Conservation Actions Importance Category Restore fish passage in dammed rivers. High Habitat Restoration/Improvement Restrict commercial harvest (Mississippi River High Population Management closed to harvest). Monitoring Strategies Monitor population distribution and abundance in large river faunal surveys in cooperation -
Esox Lucius) Ecological Risk Screening Summary
Northern Pike (Esox lucius) Ecological Risk Screening Summary U.S. Fish & Wildlife Service, February 2019 Web Version, 8/26/2019 Photo: Ryan Hagerty/USFWS. Public Domain – Government Work. Available: https://digitalmedia.fws.gov/digital/collection/natdiglib/id/26990/rec/22. (February 1, 2019). 1 Native Range and Status in the United States Native Range From Froese and Pauly (2019a): “Circumpolar in fresh water. North America: Atlantic, Arctic, Pacific, Great Lakes, and Mississippi River basins from Labrador to Alaska and south to Pennsylvania and Nebraska, USA [Page and Burr 2011]. Eurasia: Caspian, Black, Baltic, White, Barents, Arctic, North and Aral Seas and Atlantic basins, southwest to Adour drainage; Mediterranean basin in Rhône drainage and northern Italy. Widely distributed in central Asia and Siberia easward [sic] to Anadyr drainage (Bering Sea basin). Historically absent from Iberian Peninsula, Mediterranean France, central Italy, southern and western Greece, eastern Adriatic basin, Iceland, western Norway and northern Scotland.” Froese and Pauly (2019a) list Esox lucius as native in Armenia, Azerbaijan, China, Georgia, Iran, Kazakhstan, Mongolia, Turkey, Turkmenistan, Uzbekistan, Albania, Austria, Belgium, Bosnia Herzegovina, Bulgaria, Croatia, Czech Republic, Denmark, Estonia, Finland, France, Germany, Greece, Hungary, Ireland, Italy, Latvia, Lithuania, Luxembourg, Macedonia, Moldova, Monaco, 1 Netherlands, Norway, Poland, Romania, Russia, Serbia, Slovakia, Slovenia, Sweden, Switzerland, United Kingdom, Ukraine, Canada, and the United States (including Alaska). From Froese and Pauly (2019a): “Occurs in Erqishi river and Ulungur lake [in China].” “Known from the Selenge drainage [in Mongolia] [Kottelat 2006].” “[In Turkey:] Known from the European Black Sea watersheds, Anatolian Black Sea watersheds, Central and Western Anatolian lake watersheds, and Gulf watersheds (Firat Nehri, Dicle Nehri). -
Kansas Stream Fishes
A POCKET GUIDE TO Kansas Stream Fishes ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ By Jessica Mounts Illustrations © Joseph Tomelleri Sponsored by Chickadee Checkoff, Westar Energy Green Team, Kansas Department of Wildlife, Parks and Tourism, Kansas Alliance for Wetlands & Streams, and Kansas Chapter of the American Fisheries Society Published by the Friends of the Great Plains Nature Center Table of Contents • Introduction • 2 • Fish Anatomy • 3 • Species Accounts: Sturgeons (Family Acipenseridae) • 4 ■ Shovelnose Sturgeon • 5 ■ Pallid Sturgeon • 6 Minnows (Family Cyprinidae) • 7 ■ Southern Redbelly Dace • 8 ■ Western Blacknose Dace • 9 ©Ryan Waters ■ Bluntface Shiner • 10 ■ Red Shiner • 10 ■ Spotfin Shiner • 11 ■ Central Stoneroller • 12 ■ Creek Chub • 12 ■ Peppered Chub / Shoal Chub • 13 Plains Minnow ■ Silver Chub • 14 ■ Hornyhead Chub / Redspot Chub • 15 ■ Gravel Chub • 16 ■ Brassy Minnow • 17 ■ Plains Minnow / Western Silvery Minnow • 18 ■ Cardinal Shiner • 19 ■ Common Shiner • 20 ■ Bigmouth Shiner • 21 ■ • 21 Redfin Shiner Cover Photo: Photo by Ryan ■ Carmine Shiner • 22 Waters. KDWPT Stream ■ Golden Shiner • 22 Survey and Assessment ■ Program collected these Topeka Shiner • 23 male Orangespotted Sunfish ■ Bluntnose Minnow • 24 from Buckner Creek in Hodgeman County, Kansas. ■ Bigeye Shiner • 25 The fish were catalogued ■ Emerald Shiner • 26 and returned to the stream ■ Sand Shiner • 26 after the photograph. ■ Bullhead Minnow • 27 ■ Fathead Minnow • 27 ■ Slim Minnow • 28 ■ Suckermouth Minnow • 28 Suckers (Family Catostomidae) • 29 ■ River Carpsucker • -
Summary Report of Freshwater Nonindigenous Aquatic Species in U.S
Summary Report of Freshwater Nonindigenous Aquatic Species in U.S. Fish and Wildlife Service Region 4—An Update April 2013 Prepared by: Pam L. Fuller, Amy J. Benson, and Matthew J. Cannister U.S. Geological Survey Southeast Ecological Science Center Gainesville, Florida Prepared for: U.S. Fish and Wildlife Service Southeast Region Atlanta, Georgia Cover Photos: Silver Carp, Hypophthalmichthys molitrix – Auburn University Giant Applesnail, Pomacea maculata – David Knott Straightedge Crayfish, Procambarus hayi – U.S. Forest Service i Table of Contents Table of Contents ...................................................................................................................................... ii List of Figures ............................................................................................................................................ v List of Tables ............................................................................................................................................ vi INTRODUCTION ............................................................................................................................................. 1 Overview of Region 4 Introductions Since 2000 ....................................................................................... 1 Format of Species Accounts ...................................................................................................................... 2 Explanation of Maps ................................................................................................................................ -
Factors Influencing Community Structure of Riverine
FACTORS INFLUENCING COMMUNITY STRUCTURE OF RIVERINE ORGANISMS: IMPLICATIONS FOR IMPERILED SPECIES MANAGEMENT by David S. Ruppel, M.S. A dissertation submitted to the Graduate Council of Texas State University in partial fulfillment of the requirements for the degree of Doctor of Philosophy with a Major in Aquatic Resources and Integrative Biology May 2019 Committee Members: Timothy H. Bonner, Chair Noland H. Martin Joseph A. Veech Kenneth G. Ostrand James A. Stoeckel COPYRIGHT by David S. Ruppel 2019 FAIR USE AND AUTHOR’S PERMISSION STATEMENT Fair Use This work is protected by the Copyright Laws of the United States (Public Law 94-553, section 107). Consistent with fair use as defined in the Copyright Laws, brief quotations from this material are allowed with proper acknowledgement. Use of this material for financial gain without the author’s express written permission is not allowed. Duplication Permission As the copyright holder of this work I, David S. Ruppel, authorize duplication of this work, in whole or in part, for educational or scholarly purposes only. ACKNOWLEDGEMENTS First, I thank my major advisor, Timothy H. Bonner, who has been a great mentor throughout my time at Texas State University. He has passed along his vast knowledge and has provided exceptional professional guidance and support with will benefit me immensely as I continue to pursue an academic career. I also thank my committee members Dr. Noland H. Martin, Dr. Joseph A. Veech, Dr. Kenneth G. Ostrand, and Dr. James A. Stoeckel who provided great comments on my dissertation and have helped in shaping manuscripts that will be produced in the future from each one of my chapters. -
Recovery Strategy for the Western Silvery Minnow (Hybognathus Argyritis) in Canada
Species at Risk Act Recovery Strategy Series Recovery Strategy for the Western Silvery Minnow (Hypognathus argyritis) in Canada Western Silvery Minnow February 2008 About the Species at Risk Act Recovery Strategy Series What is the Species at Risk Act (SARA)? SARA is the Act developed by the federal government as a key contribution to the common national effort to protect and conserve species at risk in Canada. SARA came into force in 2003 and one of its purposes is “to provide for the recovery of wildlife species that are extirpated, endangered or threatened as a result of human activity.” What is recovery? In the context of species at risk conservation, recovery is the process by which the decline of an endangered, threatened, or extirpated species is arrested or reversed and threats are removed or reduced to improve the likelihood of the species’ persistence in the wild. A species will be considered recovered when its long-term persistence in the wild has been secured. What is a recovery strategy? A recovery strategy is a planning document that identifies what needs to be done to arrest or reverse the decline of a species. It sets goals and objectives and identifies the main areas of activities to be undertaken. Detailed planning is done at the action plan stage. Recovery strategy development is a commitment of all provinces and territories and of three federal agencies — Environment Canada, Parks Canada Agency, and Fisheries and Oceans Canada — under the Accord for the Protection of Species at Risk. Sections 37–46 of SARA (http://www.sararegistry.gc.ca/the_act/) outline both the required content and the process for developing recovery strategies published in this series. -
Feeding Preference of the Rio Grande Silvery Minnow (Hybognathus Amarus)
Reviews in Fisheries Science, 17(4):468–477, 2009 ISSN: 1064-1262 print DOI: 10.1080/10641260902985096 Feeding Preference of the Rio Grande Silvery Minnow (Hybognathus amarus) HUGO A. MAGANA USDA Forest Service, Rocky Mountain Research Station, Albuquerque, New Mexico, USA The Rio Grande silvery minnow (Hybognathus amarus) was historically the most abundant fish in the Rio Grande Basin. However, populations have been declining to the point of being listed under the Endangered Species Act. Potential causes for the decline have been studied, yet little attention has been paid to food resources. This study had three objectives: (1) Determine whether larval fish show a substrate preference when foraging. (2) Determine whether larval fish have a diatom preference when presented with 15 diatom species over six feeding trials. (3) I investigated the possibility of training/conditioning H. amarus to feed on natural food sources (diatoms) and observe conditioning response (reaction time to feeding). I found no difference between substrate preference (p = 0.26). Results for feeding trials 1, 2, and 3 revealed a preference for Nitzschia palea (p < 0.01). Trial 4 revealed a preference for N. paleaformis (p < 0.01). Navicula veneta was the preferred diatom species in feeding trial 5. Nitzschia cf. intermedia was preferred in trial 6 (p < 0.03). Results from these feeding trials proved that H. amarus larvae learn quickly and can be trained to feed on diatom cultures after only one 30-min exposure. Pre-conditioned H. amarus arrived at diatoms cultures in 49 sec ± 39 sec compared to non-conditioned H. amarus, which arrived at diatom cultures at 250 sec ± 550 sec.