Reproductive Biology of the Rio Grande Sucker Catostomus Plebeius

Total Page:16

File Type:pdf, Size:1020Kb

Reproductive Biology of the Rio Grande Sucker Catostomus Plebeius June 1995 Notes 237 PLUMMER,M. V. 1992. Relationships among moth- ards; resolution of a paradox. Amer. Nat., 112:595- ers, litters, and neonates in diamondback water 608. snakes (Nerodia rhombifer). Copeia, 1992:1096- WERNER,D. I. 1988. The effect of varying water 1098. potential on body weight, yolk and fat bodies in RAND, A. S. 1984. Clutch size in Iguana iguana in neonate green iguanas. Copeia, 1988:406-11. Central Panama. Pp. 115-122, in Vertebrate ecol- 1991. The rational use of green iguanas. ogy and systematics-a tribute to Henry S. Fitch Pp. 181-201, in Neotropical wildlife use and con- (R. A. Seigel, L., E. Hunt, J. L. Knight, L. Ma- servation (J. G. Robinson and K. H. Redford, eds.). laret, and N. L. Zuschlag, eds.). Mus. Nat. Hist., Univ. Chicago Press, Chicago, Illinois. Univ. Kansas, Lawrence. WERNER,D. I., ANDT. J. MILLER. 1984. Artificial RAND, A. S., AND H. W. GREENE. 1982. Latitude nests for female green iguanas. Herpetol. Rev., 15: and climate in the phenology of reproduction in the 57-58. green iguana, Iguana iguana. Pp. 142-149, in Igua- WIEWANDT,T. A. 1982. Evolution of nesting pat- nas of the world: behavior, ecology and conservation terns in iguanine lizards. Pp. 119-141, in Iguanas (G. M. Burghardt and S. Rand, eds.). Noyes Publ., of the world: behavior, ecology and conservation New Jersey. (G. M. Burghardt and S. Rand, eds.). Noyes Publ., Vitt, L. J. 1978. Caloric content of lizard and snake New Jersey. (Reptilia) eggs and bodies and the conversion of WILLIAMS,G. C. 1966. Adaptation and natural se- weight to caloric data. J. Herpetol., 12:65-72. lection. Princeton Univ. Press, Princeton, New Jer- VITT, L. J., ANDJ. D. CONGDON. 1978. Body shape, sey. reproductive effort, and relative clutch mass in liz- REPRODUCTIVE BIOLOGY OF THE RIO GRANDE SUCKER, CATOSTOMUS PLEBEIUS (CYPRINIFORMES), IN A MONTANE STREAM, NEW MEXICO JOHN N. RINNE United States Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station, The Southwest Forest Science Complex, 2500 South Pineknoll Drive, Flagstaf, Arizona 86001 Although the Rio Grande sucker, Catostomus spawns in spring and, in some areas, in the fall. plebeius, was first described almost a century and Although adults may grow to a large size (>40 a half ago by Baird and Girard (1854), Koster cm), most individuals are small and some mature (1957) first presented the meager known life his- when only "a few inches long." Rausch (1963) tory information for the species. It is currently examined age, growth and maturity of this suck- distributed in tributaries of the Rio Grande, pri- er. Koster (1957) suggested this species to be a marily north of the 36th parallel (Sublette et al., good bait or forage fish and that trout can and 1990). It has been introduced into the headwaters commonly do feed on this largely primary con- of the Gila River. Although substantial popula- sumer. tions are extant in New Mexico, only one occurs The Rio Grande sucker was encountered in in Colorado. The species also currently inhabits large numbers during research investigating the a half dozen river basins encompassing three states effects of grazing on nearstream and instream of Mexico (Smith, 1966; Hendrickson et al., 1980; habitat and biota in the Rio de las Vacas in north- Sublette et al., 1990). ern New Mexico (Rinne, 1988). Because there Larger individuals feed on filamentous algae is a lack of ecological and life history information and other microscopic and macroscopic organisms for Rio Grande sucker, specimens were collected such as diatoms and benthic invertebrates inhab- between 1985 and 1987, preserved, and aspects iting fast, rocky riffles (Sublette et al., 1990). of their reproductive biology were examined. This Koster (1957) reported that Rio Grande sucker paper reports information on aspects of the re- 238 The Southwestern Naturalist vol. 40, no. 2 TABLE1-Comparison of reproductivetraits of male TABLE2-Comparison of degreeof tuberculationon and female Rio Grande sucker (Catostomusplebeius) body and fins of male and female Rio Grande sucker in the Rio de las Vacas, 1985-1987. All values are (Catostomus plebeius) in the Rio de las Vacas, New means (+SE). All comparisonsare significantlydif- Mexico, 1985-1987. All values are means (+SE). ** ferent (P < 0.01). = P < 0.01. Male Female Male Female Trait n = 112 n = 99 Tuberculation n = 112 n = 99 Total length (mm1) 102.1 + 1.4 110.1 + 2.0 Body 2.7 + 0.05 3.0 Fish volume (ml) 12.7 + 0.54 16.8 + 0.07 Head 2.5 + 0.07** 3.0 + 0.02** Gonad (ml) 0.30 + 0.02 0.82 + 0.09 Caudal peduncle 2.9 + 0.03 3.0 Color index 1.5 + 0.05 1.7 + 0.04 Gular 2.6 + 0.05** 3.0 + 0.01** Gonadal index 2.3 + 0.19 4.6 + 0.34 Operculum 2.6 + 0.07 3.0 Pectoralfin 2.4 + 0.07** 3.0 + 0.02** in mm males, Range total length = 60-138 in 61- Pelvic fin 3.0 3.0 162 mm in females. Anal fin 3.0 3.0 Caudal fin 3.0 3.0 productive biology of the Rio Grande sucker in- habiting the Rio de las Vacas in Northern New Mexico. displacement. Gonadal indices (GI) were calcu- The Rio de las Vacas is a third-order montane lated by dividing gonadal volume by fish volume stream (elevation, 2,800 m) located on the Santa and multiplying the resulting value by 100. Fe- Fe National Forest, Sandoval County, about 120 cundity was estimated by removal of ovaries and km NNW of Albuquerque, New Mexico (Rinne, counting of all mature ova present in 21 females 1988, 1995). Detailed descriptions of this ripar- collected in March, June, and July, 1985 and ian-stream area are given in Rinne (1988) and with GI greater than 4.0. Szaro and Rinne (1988) and are summarized here. Presence and intensity of tuberculation and The stream is affected by typical forest manage- breeding coloration on the body and fins were ment activities such as logging, recreation, road noted relative to sex. Variation in tuberculation building, and livestock grazing. Portions of the was coded from 1 to 3 to delineate either pro- study area have been fenced to exclude livestock nounced presence (1), weak presence (2), or ab- grazing. Riparian vegetation is more abundant sence (3). Color was recorded as either present within these exclosures and is dominated by a (1) or absent (2). willow (Salix)-alder (Alnus) community. Beaver Data on reproductive traits between sexes were (Castorcanadense) inhabit the area, and damming analyzed by simple t-tests. Analysis of variance of the stream is common, however dams are not (ANOVA) was used to compare GI among sam- permanent because of annual washouts by spring ple dates. Length and GI were related by re- runoff. Streambanks are unstable in the grazed gression analyses to depict size at maturity. areas (Rinne, in litt.) and fine sediment content Of the 211 suckers collected for reproductive of the stream substrate is greater in reaches sub- analyses during the period March 1985 through jected to grazing (Rinne, 1988). June 1987, 112 were males and 99 females. Fe- Most Rio Grande suckers were collected dur- male suckers were only slightly but significantly ing annual summer sampling (June to July), with (P = 0.002) larger than males (Table 1). Sexual additional samples taken in March, April, Sep- dimorphism was also illustrated by the signifi- tember, and October 1985. Rio Grande sucker cantly greater mean volume of female than male were stunned with a direct current, backpack suckers (Table 1). electrofisher, dipnetted, and immediately pre- As in most cypriniform fishes, the presence of served in 10% formalin-sugar solution in order color was also significantly more common in males to enhance color retention in specimens. The total than in females (P < 0.001). Regression models length (TL) of preserved specimens was mea- for the sexes explained only about 25% of the sured and fish volume was estimated by liquid variation in color of suckers. By comparison, lo- displacement (ml). Gonads were then removed gistic regression produced a "best fit" model that and their volumes similarly determined by liquid included sex, month, gonad volume, and length. June 1995 Notes 239 TABLE3-Comparison of mean seasonalgonadal indices of Rio Grande suckers(Catostomus plebeius) in the Rio de las Vacas, New Mexico, 1985-1987. Sample date Male Female March' n = 5 2.12 + 1.43 n = 14 4.26 + 0.32 April n = 3 1.8 + 0.31 n= 83.83 + 0.51 June n = 20 4.07 + 0.43 n = 18 7.80 + 1.12 June n = 13 0.57 + 0.19 n = 20 2.69 + 0.58 July n = 35 3.13 + 0.19 n = 15 5.69 + 1.03 Sept n = 23 0.72 + 0.13 n = 6 3.18 + 0.30 Oct n = 13 2.18 + 0.72 n = 18 3.61 + 0.18 ' All samplesmade in 1985 except for the secondsample listed for June and the samplein September,which were made in 1987. The remaining independent variable, fish vol- yses indicated 56% of the variation in fecundity ume, was not significantly (P = 0.09) related to of suckers was explained by gonad volume. Fe- color. The fitted model for Rio Grande suckers cundity of suckers varied significantly with season in the Rio de las Vacas is: (P = 0.02) and was greatest in the autumn and least in the spring. E (the logit) = -7.0199 - 0.8614(sex) Koster (1957) previously suggested that the + 0.3829(month) Rio Grande sucker displayed a definite spring to + 0.7869(gonad volume) summer perhaps an autumnal spawn- + 0.0313(length) early and ing effort.
Recommended publications
  • Habitat Use by the Fishes of a Southwestern Desert Stream: Cherry Creek, Arizona
    ARIZONA COOPERATIVE FISH AND WILDLIFE RESEARCH UNIT SEPTEMBER 2010 Habitat use by the fishes of a southwestern desert stream: Cherry Creek, Arizona By: Scott A. Bonar, Norman Mercado-Silva, and David Rogowski Fisheries Research Report 02-10 Support Provided by: 1 Habitat use by the fishes of a southwestern desert stream: Cherry Creek, Arizona By Scott A. Bonar, Norman Mercado-Silva, and David Rogowski USGS Arizona Cooperative Fish and Wildlife Research Unit School of Natural Resources and the Environment 325 Biological Sciences East University of Arizona Tucson AZ 85721 USGS Arizona Cooperative Fish and Wildlife Unit Fisheries Research Report 02-10 Funding provided by: United States Department of Agriculture Forest Service With additional support from: School of Natural Resources and the Environment, University of Arizona Arizona Department of Game and Fish United States Geological Survey 2 Executive Summary Fish communities in the Southwest U.S. face numerous threats of anthropogenic origin. Most importantly, declining instream flows have impacted southwestern stream fish assemblages. Maintenance of water flows that sustain viable fish communities is key in maintaining the ecological function of river ecosystems in arid regions. Efforts to calculate the optimal amount of water that will ensure long-term viability of species in a stream community require that the specific habitat requirements for all species in the community be known. Habitat suitability criteria (HSC) are used to translate structural and hydraulic characteristics of streams into indices of habitat quality for fishes. Habitat suitability criteria summarize the preference of fishes for numerous habitat variables. We estimated HSC for water depth, water velocity, substrate, and water temperature for the fishes of Cherry Creek, Arizona, a perennial desert stream.
    [Show full text]
  • Seasonal and Diel Movements and Habitat Use of Robust Redhorses in the Lower Savannah River. Georgia, and South Carolina
    Transactions of the American FisheriesSociety 135:1145-1155, 2006 [Article] © Copyright by the American Fisheries Society 2006 DO: 10.1577/705-230.1 Seasonal and Diel Movements and Habitat Use of Robust Redhorses in the Lower Savannah River, Georgia and South Carolina TIMOTHY B. GRABOWSKI*I Department of Biological Sciences, Clemson University, Clemson, South Carolina,29634-0326, USA J. JEFFERY ISELY U.S. Geological Survey, South Carolina Cooperative Fish and Wildlife Research Unit, Clemson University, Clemson, South Carolina, 29634-0372, USA Abstract.-The robust redhorse Moxostonta robustum is a large riverine catostomid whose distribution is restricted to three Atlantic Slope drainages. Once presumed extinct, this species was rediscovered in 1991. Despite being the focus of conservation and recovery efforts, the robust redhorse's movements and habitat use are virtually unknown. We surgically implanted pulse-coded radio transmitters into 17 wild adults (460-690 mm total length) below the downstream-most dam on the Savannah River and into 2 fish above this dam. Individuals were located every 2 weeks from June 2002 to September 2003 and monthly thereafter to May 2005. Additionally, we located 5-10 individuals every 2 h over a 48-h period during each season. Study fish moved at least 24.7 ± 8.4 river kilometers (rkm; mean ± SE) per season. This movement was generally downstream except during spring. Some individuals moved downstream by as much as 195 rkm from their release sites. Seasonal migrations were correlated to seasonal changes in water temperature. Robust redhorses initiated spring upstream migrations when water temperature reached approximately 12'C. Our diel tracking suggests that robust redhorses occupy small reaches of river (- 1.0 rkm) and are mainly active diumally.
    [Show full text]
  • Edna Assay Development
    Environmental DNA assays available for species detection via qPCR analysis at the U.S.D.A Forest Service National Genomics Center for Wildlife and Fish Conservation (NGC). Asterisks indicate the assay was designed at the NGC. This list was last updated in June 2021 and is subject to change. Please contact [email protected] with questions. Family Species Common name Ready for use? Mustelidae Martes americana, Martes caurina American and Pacific marten* Y Castoridae Castor canadensis American beaver Y Ranidae Lithobates catesbeianus American bullfrog Y Cinclidae Cinclus mexicanus American dipper* N Anguillidae Anguilla rostrata American eel Y Soricidae Sorex palustris American water shrew* N Salmonidae Oncorhynchus clarkii ssp Any cutthroat trout* N Petromyzontidae Lampetra spp. Any Lampetra* Y Salmonidae Salmonidae Any salmonid* Y Cottidae Cottidae Any sculpin* Y Salmonidae Thymallus arcticus Arctic grayling* Y Cyrenidae Corbicula fluminea Asian clam* N Salmonidae Salmo salar Atlantic Salmon Y Lymnaeidae Radix auricularia Big-eared radix* N Cyprinidae Mylopharyngodon piceus Black carp N Ictaluridae Ameiurus melas Black Bullhead* N Catostomidae Cycleptus elongatus Blue Sucker* N Cichlidae Oreochromis aureus Blue tilapia* N Catostomidae Catostomus discobolus Bluehead sucker* N Catostomidae Catostomus virescens Bluehead sucker* Y Felidae Lynx rufus Bobcat* Y Hylidae Pseudocris maculata Boreal chorus frog N Hydrocharitaceae Egeria densa Brazilian elodea N Salmonidae Salvelinus fontinalis Brook trout* Y Colubridae Boiga irregularis Brown tree snake*
    [Show full text]
  • Rio Grande National Forest Draft Assessment 5 At-Risk Species
    Rio Grande National Forest- Draft Assessment 5 Identifying and Assessing At-risk Species Rio Grande National Forest Draft Assessment 5 Identifying and Assessing At-risk Species Contents Introduction .............................................................................................................................................. 1 Information Sources and Gaps .............................................................................................................. 2 Existing Forest Plan Direction .............................................................................................................. 2 Scale of Analysis (Area of Influence) ................................................................................................... 4 Assessment 5 Development Process ..................................................................................................... 4 Federally Recognized Species .................................................................................................................. 6 Uncompahgre Fritillary Butterfly ......................................................................................................... 6 Black-footed Ferret ............................................................................................................................... 8 Canada Lynx ....................................................................................................................................... 11 New Mexico Meadow Jumping Mouse .............................................................................................
    [Show full text]
  • Rio Costilla Habitat Improvement Project
    Decision Memo Rio Costilla Habitat Improvement Project USDA Forest Service, Southwestern Region Questa Ranger District, Carson National Forest Taos County, New Mexico (Sections 1, 2, 11, 12, 14, and 15 of Township 30 North, Range 15 East) Background An interdisciplinary analysis on this project was conducted and is documented in a project record. Source documents from the project record are incorporated by reference throughout this decision memo by showing the document number in brackets [PR #]. Please refer to Appendix A for the project record index. The Questa Ranger District of the Carson National Forest, in partnership with the New Mexico Department of Game and Fish (NMDGF) and the U.S. Fish and Wildlife Service, proposes to improve in- stream habitat conditions within the Rio Costilla [PR #77, 128]. The Valle Vidal Unit of the Carson National Forest attracts hundreds of anglers annually. The Rio Costilla is the largest stream in the Valle Vidal and a favorite among anglers. Anglers travel to this area in large part to pursue the native Rio Grande cutthroat trout. Long-term operations of the Costilla Reservoir and Dam have channelized the Rio Costilla, which has become inadequate for holding fish during low-flow conditions and through the winter. The Rio Costilla has become shallow and wide in many spots, and future efforts to re-establish self-sustaining populations of Rio Grande cutthroat trout may not be successful without active management. Since 2001, Rio Grande cutthroat trout and other native fish population restoration efforts have been ongoing within the upper Rio Costilla watershed. Restoration efforts in this section of the Rio Costilla have included the construction of the Rio Costilla terminal fish barrier in October 2016.
    [Show full text]
  • Three-Species Investigations Kevin Thompson Aquatic Research
    Three-Species Investigations Kevin Thompson Aquatic Research Scientist Job Progress Report Colorado Parks & Wildlife Aquatic Research Section Fort Collins, Colorado May 2017 STATE OF COLORADO John W. Hickenlooper, Governor COLORADO DEPARTMENT OF NATURAL RESOURCES Bob Randall, Executive Director COLORADO PARKS & WILDLIFE Bob Broscheid, Director WILDLIFE COMMISSION Chris Castilian, Chair Robert William Bray Jeanne Horne, Vice-Chair John V. Howard, Jr. James C. Pribyl, Secretary James Vigil William G. Kane Dale E. Pizil Robert “Dean” Wingfield Michelle Zimmerman Alexander Zipp Ex Officio/Non-Voting Members: Don Brown, Bob Randall and Bob Broscheid AQUATIC RESEARCH STAFF George J. Schisler, Aquatic Research Leader Kelly Carlson, Aquatic Research Program Assistant Peter Cadmus, Aquatic Research Scientist/Toxicologist, Water Pollution Studies Eric R. Fetherman, Aquatic Research Scientist, Salmonid Disease Studies Ryan Fitzpatrick, Aquatic Research Scientist, Eastern Plains Native Fishes Eric E. Richer, Aquatic Research Scientist/Hydrologist, Stream Habitat Restoration Matthew C. Kondratieff, Aquatic Research Scientist, Stream Habitat Restoration Dan Kowalski, Aquatic Research Scientist, Stream & River Ecology Adam Hansen, Aquatic Research Scientist, Coldwater Lakes and Reservoirs Kevin B. Rogers, Aquatic Research Scientist, Colorado Cutthroat Studies Kevin G. Thompson, Aquatic Research Scientist, 3-Species and Boreal Toad Studies Andrew J. Treble, Aquatic Research Scientist, Aquatic Data Management and Analysis Brad Neuschwanger, Hatchery Manager,
    [Show full text]
  • Influence of Non-Native Trout on Native Non-Game Fish in Nebraska Headwater Streams" (2014)
    University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Dissertations & Theses in Natural Resources Natural Resources, School of 5-2014 Influence of Non-Native Trout on Native Non- Game Fish in Nebraska Headwater Streams Kelly C. Turek University of Nebraska-Lincoln, [email protected] Follow this and additional works at: http://digitalcommons.unl.edu/natresdiss Part of the Aquaculture and Fisheries Commons Turek, Kelly C., "Influence of Non-Native Trout on Native Non-Game Fish in Nebraska Headwater Streams" (2014). Dissertations & Theses in Natural Resources. 90. http://digitalcommons.unl.edu/natresdiss/90 This Article is brought to you for free and open access by the Natural Resources, School of at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Dissertations & Theses in Natural Resources by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. INFLUENCE OF NON-NATIVE TROUT ON NATIVE NON-GAME FISH IN NEBRASKA HEADWATER STREAMS By Kelly C. Turek A THESIS Presented to the Faculty of The Graduate College at the University of Nebraska In Partial Fulfillment of Requirements For the Degree of Master of Science Major: Natural Resource Sciences Under the Supervision of Professors Mark A. Pegg and Kevin L. Pope Lincoln, Nebraska May, 2014 INFLUENCE OF NON-NATIVE TROUT ON NATIVE NON-GAME FISH IN NEBRASKA HEADWATER STREAMS Kelly C. Turek, M.S. University of Nebraska, 2014 Advisors: Mark A. Pegg and Kevin L. Pope Introduced, non-native trout may have detrimental competitive or predatory interactions with native fishes. However, few studies have experimentally examined interactions between introduced trout and native non-game species.
    [Show full text]
  • 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
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • Endangered and Threatened Animals of Utah
    Endangered and Threatened Animals of Utah Quinney Professorship for Wildlife Conflict Management Jack H. Berryman Institute U.S. Fish and Wildlife Service Utah Department of Natural Resources Division of Wildlife Resources Utah State University Extension Service Endangered and Threatened Animals of Utah 1998 Acknowledgments This publication was produced by Utah State University Extension Service Department of Fisheries and Wildlife The Jack H. Berryman Institute Utah Division of Wildlife U.S. Fish and Wildlife Service Office of Extension and Publications Contributing Authors Purpose and Introduction Terry Messmer Marilet Zablan Mammals Boyde Blackwell Athena Menses Birds Frank Howe Fishes Leo Lentsch Terry Messmer Richard Drake Reptiles and Invertebrates Terry Messmer Richard Drake Utah Sensitive Species List Frank Howe Editors Terry Messmer Richard Drake Audrey McElrone Publication Publication Assistance by Remani Rajagopal Layout and design by Gail Christensen USU Publication Design and Production Quinney Professorship for Wildlife Conflict Management This bulletin was developed under the auspices of the Quinney Professorship for Wildlife Conflict Management through the sponsorship of the S. J. and Jessie E. Quinney Foundation in partnership with the College of Natural Resources, Jack H. Berryman Institute for Wild- life Damage Management, U.S. Fish and Wildlife Service, Utah Department of Natural Resources, and Utah Division of Wildlife Resources. i Contents Purpose of this Guide . iii Introduction . v What are endangered and threatened species? . vi Why some species become endangered or threatened? . vi Why protect endangered species? . vi The Federal Endangered Species Act of 1973 (ESA) . viii Mammals Black-footed Ferret . 1 Grizzly Bear . 5 Gray Wolf . 9 Utah Prairie Dog . 13 Birds Bald Eagle .
    [Show full text]
  • Habitat Selection of Robust Redhorse Moxostoma Robustum
    HABITAT SELECTION OF ROBUST REDHORSE MOXOSTOMA ROBUSTUM : IMPLICATIONS FOR DEVELOPING SAMPLING PROTOCOLS by DIARRA LEMUEL MOSLEY (Under the Direction of Cecil A. Jennings) ABSTRACT Robust Redhorse, described originally in 1870, went unnoticed until 1991 when they were rediscovered in the lower Oconee River, Georgia. This research evaluated one hypothesis (habitat use) for explaining the absence of juveniles (30 mm – 410 mm TL) from samples of wild-caught robust redhorse. Two mesocosms were used to determine if juvenile robust redhorse use available habitats proportionately. Pond-reared juveniles were exposed to four, flow-based habitats (eddies = - 0.12 to -0.01 m/s, slow flow = 0.00 to 0.15 m/s, moderate flow = 0.16 to 0.32 m/s, and backwaters). Location data were recorded for each fish, and overall habitat use was evaluated with a Log-Linear Model. In winter, the fish preferred eddies and backwaters. In early spring the fish preferred eddies. Catch of wild juveniles may be improved by sampling eddies and their associated transitional areas. INDEX WORDS: backwaters, catostomid, eddies, habitat selection, juvenile fish, mesocosm, Moxostoma robustum, Oconee River, robust redhorse HABITAT SELECTION OF ROBUST REDHORSE MOXOSTOMA ROBUSTUM : IMPLICATIONS FOR DEVELOPING SAMPLING PROTOCOLS by DIARRA LEMUEL MOSLEY BSFR, University of Georgia, 1998 A Thesis Submitted to the Graduate Faculty of The University of Georgia in Partial Fulfillment of the Requirements for the Degree MASTER OF SCIENCE ATHENS, GEORGIA 2006 © 2006 Diarra Lemuel Mosley All Rights Reserved HABITAT SELECTION OF ROBUST REDHORSE MOXOSTOMA ROBUSTUM : IMPLICATIONS FOR DEVELOPING SAMPLING PROTOCOLS by DIARRA LEMUEL MOSLEY Major Professor: Cecil A.
    [Show full text]