3.2.11 Bothriocephalosis - 1
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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. -
From the Western Mosquitofish, Gambusia Affinis (Cyprinodontiformes: Poeciliidae): New Distributional Records for Arkansas, Kansas and Oklahoma
42 Salsuginus seculus (Monogenoidea: Dactylogyrida: Ancyrocephalidae) from the Western Mosquitofish, Gambusia affinis (Cyprinodontiformes: Poeciliidae): New distributional records for Arkansas, Kansas and Oklahoma Chris T. McAllister Science and Mathematics Division, Eastern Oklahoma State College, Idabel, OK 74745 Donald G. Cloutman P. O. Box 197, Burdett, KS 67523 Henry W. Robison Department of Biology, Southern Arkansas University, Magnolia, AR 71754 Studies on fish monogeneans in Oklahoma and S. fundulus (Mizelle) Murith and Beverley- are relatively uncommon (Seamster 1937, 1938, Burton in Northern Studfish,Fundulus catenatus 1960; Mizelle 1938; Monaco and Mizelle 1955; (McAllister et al. 2015, 2016). In Kansas, a McDaniel 1963; McDaniel and Bailey 1966; single species, S. thalkeni Janovy, Ruhnke, and Wheeler and Beverley-Burton 1989) with little Wheeler (syn. S. fundulus) has been reported or no published work in the past two decades from Northern Plains Killifish,Fundulus kansae or more. Members of the ancyrocephalid (see Janovy et al. 1989). Here, we report genus Salsuginus (Beverley-Burton) Murith new distributional records for a species of and Beverley-Burton have been reported Salsuginus in Arkansas, Kansas and Oklahoma. from various fundulid fishes including those from Alabama, Arkansas, Illinois, Kentucky, During June 1983 (Kansas only) and again Nebraska, New York, Tennessee, and Texas, between April 2014 and September 2015, and Newfoundland and Ontario, Canada, 36 Western Mosquitofish, Gambusia affinis and the Bahama Islands; additionally, two were collected by dipnet, seine (3.7 m, 1.6 species have been reported from the Western mm mesh) or backpack electrofisher from Big Mosquitofish, Gambusia affinis (Poeciliidae) Spring at Spring Mill, Independence County, from California, Louisiana, and Texas, and Arkansas (n = 4; 35.828152°N, 91.724273°W), the Bahama Islands (see Hoffman 1999). -
RFP No. 212F for Endangered Species Research Projects for the Prairie Chub
1 RFP No. 212f for Endangered Species Research Projects for the Prairie Chub Final Report Contributing authors: David S. Ruppel, V. Alex Sotola, Ozlem Ablak Gurbuz, Noland H. Martin, and Timothy H. Bonner Addresses: Department of Biology, Texas State University, San Marcos, Texas 78666 (DSR, VAS, NHM, THB) Kirkkonaklar Anatolian High School, Turkish Ministry of Education, Ankara, Turkey (OAG) Principal investigators: Timothy H. Bonner and Noland H. Martin Email: [email protected], [email protected] Date: July 31, 2017 Style: American Fisheries Society Funding sources: Texas Comptroller of Public Accounts, Turkish Ministry of Education- Visiting Scholar Program (OAG) Summary Four hundred mesohabitats were sampled from 36 sites and 20 reaches within the upper Red River drainage from September 2015 through September 2016. Fishes (N = 36,211) taken from the mesohabitats represented 14 families and 49 species with the most abundant species consisting of Red Shiner Cyprinella lutrensis, Red River Shiner Notropis bairdi, Plains Minnow Hybognathus placitus, and Western Mosquitofish Gambusia affinis. Red River Pupfish Cyprinodon rubrofluviatilis (a species of greatest conservation need, SGCN) and Plains Killifish Fundulus zebrinus were more abundant within prairie streams (e.g., swift and shallow runs with sand and silt substrates) with high specific conductance. Red River Shiner (SGCN), Prairie Chub Macrhybopsis australis (SGCN), and Plains Minnow were more abundant within prairie 2 streams with lower specific conductance. The remaining 44 species of fishes were more abundant in non-prairie stream habitats with shallow to deep waters, which were more common in eastern tributaries of the upper Red River drainage and Red River mainstem. Prairie Chubs comprised 1.3% of the overall fish community and were most abundant in Pease River and Wichita River. -
Northern Plains Killifish - Fundulus Kansae Abundance: Common Status: NSS3 (Bb) Natureserve: G5 S5 Population Status: Stable
Northern plains Killifish - Fundulus kansae Abundance: Common Status: NSS3 (Bb) NatureServe: G5 S5 Population Status: Stable. Distribution and abundance appears stable over last decade. Limiting Factor: Habitat: severe due to limited availability of shallow, sandy habitats. Comment: Changed from NSS4 to NSS3 in 2017 due to recent surveys indicating that the distribution of this species is more restricted than previously believed within native range. Introduction The northern plains killifish is native to the Great Plains region of central North America, where it ranges from southeast Montana, South Dakota, and Missouri south to Texas (Rahel and Thel 2004). Populations have been introduced in Colorado, Utah, Arizona, New Mexico, Montana, Wyoming, Texas, and South Dakota (Rahel and Thel 2004). In Wyoming, northern plains killifish are indigenous to the North Platte and South Platte drainages, but are also found outside their range in the Big Horn and Cheyenne river drainages (Baxter and Stone 1995), possibly introduced by bait fisherman (Baxter and Simon 1970). Baxter and Simon (1970) reported no findings of northern plains killifish within the Powder River basin during 1964 sampling. Patton (1997) was the first to record the presence of this species in the Powder River system. Given this, they are likely not native to the Powder River drainage. Northern plains killifish are typically carnivorous, consuming a variety of insects and other aquatic invertebrates, and occasionally eat plant material and diatoms (Minckley and Klaassen 1969; Pflieger 1997; Rahel and Thel 2004). They feed at the surface, in the water column, and from the bottom substrate (Baxter and Stone 1995). Spawning takes place from May to August and may be stimulated by temperature and flow cues (Pflieger 1997; Rahel and Thel 2004). -
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. -
Santa Fe National Forest
Chapter 1: Introduction In Ecological and Biological Diversity of National Forests in Region 3 Bruce Vander Lee, Ruth Smith, and Joanna Bate The Nature Conservancy EXECUTIVE SUMMARY We summarized existing regional-scale biological and ecological assessment information from Arizona and New Mexico for use in the development of Forest Plans for the eleven National Forests in USDA Forest Service Region 3 (Region 3). Under the current Planning Rule, Forest Plans are to be strategic documents focusing on ecological, economic, and social sustainability. In addition, Region 3 has identified restoration of the functionality of fire-adapted systems as a central priority to address forest health issues. Assessments were selected for inclusion in this report based on (1) relevance to Forest Planning needs with emphasis on the need to address ecosystem diversity and ecological sustainability, (2) suitability to address restoration of Region 3’s major vegetation systems, and (3) suitability to address ecological conditions at regional scales. We identified five assessments that addressed the distribution and current condition of ecological and biological diversity within Region 3. We summarized each of these assessments to highlight important ecological resources that exist on National Forests in Arizona and New Mexico: • Extent and distribution of potential natural vegetation types in Arizona and New Mexico • Distribution and condition of low-elevation grasslands in Arizona • Distribution of stream reaches with native fish occurrences in Arizona • Species richness and conservation status attributes for all species on National Forests in Arizona and New Mexico • Identification of priority areas for biodiversity conservation from Ecoregional Assessments from Arizona and New Mexico Analyses of available assessments were completed across all management jurisdictions for Arizona and New Mexico, providing a regional context to illustrate the biological and ecological importance of National Forests in Region 3. -
ECOLOGY of NORTH AMERICAN FRESHWATER FISHES
ECOLOGY of NORTH AMERICAN FRESHWATER FISHES Tables STEPHEN T. ROSS University of California Press Berkeley Los Angeles London © 2013 by The Regents of the University of California ISBN 978-0-520-24945-5 uucp-ross-book-color.indbcp-ross-book-color.indb 1 44/5/13/5/13 88:34:34 AAMM uucp-ross-book-color.indbcp-ross-book-color.indb 2 44/5/13/5/13 88:34:34 AAMM TABLE 1.1 Families Composing 95% of North American Freshwater Fish Species Ranked by the Number of Native Species Number Cumulative Family of species percent Cyprinidae 297 28 Percidae 186 45 Catostomidae 71 51 Poeciliidae 69 58 Ictaluridae 46 62 Goodeidae 45 66 Atherinopsidae 39 70 Salmonidae 38 74 Cyprinodontidae 35 77 Fundulidae 34 80 Centrarchidae 31 83 Cottidae 30 86 Petromyzontidae 21 88 Cichlidae 16 89 Clupeidae 10 90 Eleotridae 10 91 Acipenseridae 8 92 Osmeridae 6 92 Elassomatidae 6 93 Gobiidae 6 93 Amblyopsidae 6 94 Pimelodidae 6 94 Gasterosteidae 5 95 source: Compiled primarily from Mayden (1992), Nelson et al. (2004), and Miller and Norris (2005). uucp-ross-book-color.indbcp-ross-book-color.indb 3 44/5/13/5/13 88:34:34 AAMM TABLE 3.1 Biogeographic Relationships of Species from a Sample of Fishes from the Ouachita River, Arkansas, at the Confl uence with the Little Missouri River (Ross, pers. observ.) Origin/ Pre- Pleistocene Taxa distribution Source Highland Stoneroller, Campostoma spadiceum 2 Mayden 1987a; Blum et al. 2008; Cashner et al. 2010 Blacktail Shiner, Cyprinella venusta 3 Mayden 1987a Steelcolor Shiner, Cyprinella whipplei 1 Mayden 1987a Redfi n Shiner, Lythrurus umbratilis 4 Mayden 1987a Bigeye Shiner, Notropis boops 1 Wiley and Mayden 1985; Mayden 1987a Bullhead Minnow, Pimephales vigilax 4 Mayden 1987a Mountain Madtom, Noturus eleutherus 2a Mayden 1985, 1987a Creole Darter, Etheostoma collettei 2a Mayden 1985 Orangebelly Darter, Etheostoma radiosum 2a Page 1983; Mayden 1985, 1987a Speckled Darter, Etheostoma stigmaeum 3 Page 1983; Simon 1997 Redspot Darter, Etheostoma artesiae 3 Mayden 1985; Piller et al. -
Pallid Sturgeon Recovery Plan
U.S. Fish & Wildlife Service Revised RECOVERY PLAN for the Pallid Sturgeon (Scaphirhynchus albus) Original Plan Approved: November 1993 Prepared by: Pallid Sturgeon Recovery Coordinator U.S. Fish and Wildlife Service Montana Fish and Wildlife Conservation Office Billings, Montana For Mountain-Prairie Region U.S. Fish and Wildlife Service Denver, CO January 2014 DISCLAIMER Recovery plans delineate reasonable actions that are believed necessary to recover and/or protect listed species. Plans are prepared by the U.S. Fish and Wildlife Service, sometimes with the assistance of recovery teams, contractors, State agencies, and others. Plans are reviewed by the public and subject to additional peer review before they are adopted by the U.S. Fish and Wildlife Service. Objectives will only be attained and funds expended contingent upon appropriations, priorities, and other budgetary constraints. Recovery plans do not obligate other parties to undertake specific tasks. Recovery plans do not necessarily 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. They represent the official position of the U.S. Fish and Wildlife Service only after they have been signed by the 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. Copies of all documents reviewed in development of the plan are available in the administrative record, located at the U.S. Fish and Wildlife Service’s Montana Fish and Wildlife Conservation Office, Billings, Montana. -
FISH of the COLORADO RIVER Colorado River and Tributaries Between Glen Canyon Dam and Lake Mead
FISH OF THE COLORADO RIVER Colorado River and tributaries between Glen Canyon Dam and Lake Mead ON-LINE TRAINING: DRAFT Outline: • Colorado River • Glen Canyon Dam Adaptive Management Program (GCDAMP) • Native Fishes • Common Non-Native Fishes • Rare Non-Native Fishes • Standardized Sampling Protocol Colorado River: • The Colorado River through Grand Canyon historically hosted one of the most distinct fish assemblages in North America (lowest diversity, highest endemism) • Aquatic habitat was variable ▫ Large spring floods ▫ Cold winter temperatures ▫ Warm summer temperatures ▫ Heavy silt load • Today ▫ Stable flow releases ▫ Cooler temperatures ▫ Predation Overview: • The Glen Canyon Dam Adaptive Management Program was established in 1997 to address downstream ecosystem impacts from operation of Glen Canyon Dam and to provide research and monitoring of downstream resources. Area of Interest: from Glen Canyon Dam to Lake Mead Glen Canyon Dam Adaptive Management Program (Fish) Goals: • Maintain or attain viable populations of existing native fish, eliminate risk of extinction from humpback chub and razorback sucker, and prevent adverse modification to their critical habitat. • Maintain a naturally reproducing population of rainbow trout above the Paria River, to the extent practicable and consistent with the maintenance of viable populations of native fish. Course Purpose: • The purpose of this training course “Fish of the Colorado River” is to provide a general overview of fish located within the Colorado River below Glen Canyon Dam downstream to Lake Mead and linked directly to the GCDAMP. • Also included are brief explanations of management concerns related to the native fish species, as well as species locations. Native Fishes: Colorado River and tributaries between Glen Canyon Dam and Lake Mead Bluehead Sucker • Scientific name: Catostomus discobolus • Status: Species of Special Concern (conservation status may be at risk) • Description: Streamlined with small scales. -
Species Status Assessment Report for the Sharpnose Shiner (Notropis Oxyrhynchus) and Smalleye Shiner (N
Species Status Assessment Report For the Sharpnose Shiner (Notropis oxyrhynchus) And Smalleye Shiner (N. buccula) Prepared by the Arlington, Texas Ecological Services Field Office U.S. Fish and Wildlife Service Date of last revision: June 10, 2014 EXECUTIVE SUMMARY This species status assessment reports the results of the comprehensive status review for the sharpnose shiner (Notropis oxyrhynchus) and smalleye shiner (N. buccula) and provides a thorough account of the species’ overall viability and, conversely, extinction risk. Sharpnose and smalleye shiners are small minnows currently restricted to the contiguous river segments of the upper Brazos River basin in north-central Texas. In conducting our status assessment we first considered what the two shiners need to ensure viability. We generally define viability as the ability of the species to persist over the long term and, conversely, to avoid extinction. We then evaluated whether those needs currently exist and the repercussions to the species when those needs are missing, diminished, or inaccessible. We next consider the factors that are causing the species to lack what it needs, included historical, current, and future factors. Finally, considering the information reviewed, we evaluated the current status and future viability of the species in terms of resiliency, redundancy, and representation. Resiliency is the ability of the species to withstand stochastic events and, in the case of the shiners, is best measured by the extent of suitable habitat in terms of stream length. Redundancy is the ability of a species to withstand catastrophic events by spreading the risk and can be measured through the duplication and distribution of resilient populations across its range. -
Parasites of Native and Non-Native Fishes in the Little Colorado River
1 Parasites of native and non-native fishes of the Little Colorado River, Grand Canyon, Arizona. Anindo Choudhury1, Timothy L. Hoffnagle2, and Rebecca A. Cole USGS-National Wildlife Health Center, 6006 Schroeder Road, Madison, WI 53711, U.S.A. 2Oregon Department of Fish and Wildlife, 211 Inlow Hall, Eastern Oregon University, La Grande, OR 97850 Corresponding author: Rebecca Cole, USGS – National Wildlife Health Center, 6006 Schroeder Road, Madison, Wisconsin 53711, U.S.A. Phone: (608) 270 2468. E-mail: [email protected]. 1Current address: Division of Natural Sciences, St. Norbert College, 100 Grant Street, DePere, Wisconsin 54115, U.S.A. Running Head: Fish parasites in the Little Colorado River. 2 ABSTRACT: A 2-year, seasonal, parasitological study of 1435 fish, belonging to 4 species of native fishes and 7 species of non-native fishes from the lower Little Colorado River (LCR) and tributary creeks, Grand Canyon, Arizona, yielded 17 (possibly 18) species of parasites. These comprised 1 myxozoan (Henneguya exilis), 2 copepods (Ergasilus arthrosis and Lernaea cyprinacea), 1 acarine (Oribatida gen. sp.), 1 piscicolid leech (Myzobdella lugubris), 3 (possibly 4) monogeneans ( Gyrodactylus hoffmani, Gyrodactylus sp., Dactylogyrus extensus, and Ligictaluridus floridanus), 4 nematodes (Contracacecum sp., Eustrongylides sp. Rhabdochona sp., Truttaedacnitis truttae), 3 cestodes (Bothriocephalus acheilognathi, Corallobothrium fimbriatum and Megathylacoides giganteum), and 2 trematodes (Ornithodiplostomum sp., Posthodiplostomum sp.). Of these, Rhabdochona sp. is the only adult parasite native to the LCR. Infection intensities (worm burden) of Ornithodiplostomum sp and B. acheilognathi were positively correlated with length of humpback chub, Gila cypha. Adult helminths showed a high degree of host specificity, the exception being B. -
(Gila Elegans) (BONY) Basic Conceptual Ecological Model for the Lower Colorado River
Bonytail (Gila elegans) (BONY) Basic Conceptual Ecological Model for the Lower Colorado River 2018 Updates 1. Eggs & Early Larvae G1-2 R5-1 S1-2 5. Spawning 2. Fry & Adults Juveniles S5-4 G2-4 G4-4 P4-5 S2-4 S4-4 4. Established Adults G3-4 3. Newly- S3-4 Stocked SHR Adults Photo courtesy of the Bureau of Reclamation March 2019 Lower Colorado River Multi-Species Conservation Program Steering Committee Members Federal Participant Group California Participant Group Bureau of Reclamation California Department of Fish and Wildlife U.S. Fish and Wildlife Service City of Needles National Park Service Coachella Valley Water District Bureau of Land Management Colorado River Board of California Bureau of Indian Affairs Bard Water District Western Area Power Administration Imperial Irrigation District Los Angeles Department of Water and Power Palo Verde Irrigation District Arizona Participant Group San Diego County Water Authority Southern California Edison Company Arizona Department of Water Resources Southern California Public Power Authority Arizona Electric Power Cooperative, Inc. The Metropolitan Water District of Southern Arizona Game and Fish Department California Arizona Power Authority Central Arizona Water Conservation District Cibola Valley Irrigation and Drainage District Nevada Participant Group City of Bullhead City City of Lake Havasu City Colorado River Commission of Nevada City of Mesa Nevada Department of Wildlife City of Somerton Southern Nevada Water Authority City of Yuma Colorado River Commission Power Users Electrical District