Electrophoretic Comparison of Cyprinodon Variegatus Lacã©Pã

Total Page:16

File Type:pdf, Size:1020Kb

Electrophoretic Comparison of Cyprinodon Variegatus Lacã©Pã Northeast Gulf Science Volume 6 Article 3 Number 2 Number 2 10-1983 Electrophoretic Comparison of Cyprinodon variegatus Lacépède and Cyprinodon hubbsi Carr, with Comments on the Genus Cyprinodon (Atheriniformes: Cyprinodontidae) Charles F. Duggins Jr. Cameron University Alvan A. Karlin Tall Timbers Research Station Kenneth G. Relyea Kuwait University DOI: 10.18785/negs.0602.03 Follow this and additional works at: https://aquila.usm.edu/goms Recommended Citation Duggins, C. F. Jr., A. A. Karlin and K. G. Relyea. 1983. Electrophoretic Comparison of Cyprinodon variegatus Lacépède and Cyprinodon hubbsi Carr, with Comments on the Genus Cyprinodon (Atheriniformes: Cyprinodontidae). Northeast Gulf Science 6 (2). Retrieved from https://aquila.usm.edu/goms/vol6/iss2/3 This Article is brought to you for free and open access by The Aquila Digital Community. It has been accepted for inclusion in Gulf of Mexico Science by an authorized editor of The Aquila Digital Community. For more information, please contact [email protected]. Duggins et al.: Electrophoretic Comparison of Cyprinodon variegatus Lacépède and Northeast Gulf Science, Vol. 6, No.2, p. 99-107 October 1983 ELECTROPHORETIC,. COMPARISON OF Cyprinodon variegatus LACEPEDE- AND Cyprinodon hubbsi CARR, WITH COMMENTS ON THE GENUS Cyprinodon (Atheriniformes: Cyprinodontidae) Charles F. Duggins, Jr. Department of Biology Cameron University Lawton, OK 73505 Alvan A. Karlin Tall Timbers Research Station Route 1, Box 160 Tallahassee, FL 32312 and Kenneth G. Relyea P.O. Box 5969 Zoology Department Kuwait University Kuwait Abstract: Five populations of Cyprinodon hubbsi were electrophoretically compared to 12 popula· tions from Florida of C. variegatus. Our data support Johnson and Snelson's (1978) placing of C. hubbsi in synonymy with C. variegatus. Present day populations of the nominal C. hubbsi possibly arose from 3 different founding populations: one derived from a Gulf coast C. variegatus popula· tion, another derived from a Florida east coast C. variegatus population, and a third from which the present day Lake Dora population of C. hubbsi is derived, origin uncertain. The large amount of morphological variation in this genus is also partially reflected electrophoretically, and the popula· tions sampled fall into discrete groups. A remarkable array of pupfish Echelle, 1975; Liu, 1969; Smith and Miller, species, genus Cyprinodon, occur in the 1980; Humphries and Miller, 1981; Saltz United States, Mexico, the Bahama Islands and Hirshfield, 1981. and on some Caribbean Islands. Most Cyprinodon variegatus Lacepede, the species, some as yet undescribed, are sheepshead minnow, ranges from geographically restricted, allopatric Massachusetts southward along the populations. Only Cyprinodon variegatus Atlantic coast through the Florida Keys, has a wide distribution, and a number of throughout the Gulf of Mexico to nominal allopatric species are seemingly northeastern Mexico, and disjunctly in related to it, constituting a "variegatus Yucatan (as C. v. artifrons, Hubbs, 1936). complex" within the genus. For details of Additional populations in the Bahamas the "variegatus complex" and for other and on Caribbean Islands have been con­ pupfish species see Turner and Liu, 1977; sidered as subspecies of C. variegatus or Miller, 1948, 1968, 1976, 1981; Echelle and as related species within the "variegatus Miller, 1974; Echelle and Echelle, 1978; complex" (Turner and Liu, 1977). Hubbs Echelle, 1975; Turner, 1973, 1974; Miller and (1936) delineated northern and southern 99 Published by The Aquila Digital Community, 1983 1 Gulf of Mexico Science, Vol. 6 [1983], No. 2, Art. 3 100 C.F. Duggins, Jr., A.A. Karlin, and K. G. Relyea subspecies, C. v. ovinus, Massachusetts to considered in this paper, is a freshwater North Carolina, and C. v. variegatus, North form. Carolina to northeastern Mexico, as well Cyprinodon hubbsi Carr is known only as C. v. artifrons from Yucatan. Earlier, Jor­ from a few central Florida lakes: Lake dan (1884) had placed populations in Cuba Eustis (type locality; Carr, 1936), Lakes and the Florida Keys in the subspecies C. Dora, Griffin, Harris, Yale, Weir and Silver v. riverendi. No published data support (Relyea, 1975; Johnson and Snelson, 1978). these subspecific allocations, nor are there All of these lakes are interconnected by any published definitive studies, other than canals and ditches and are drained by the original descriptions earlier in the century, Ocklawaha River, a western tributary of the of outlying allopatric populations in the St. Johns River. However, the canals are complex in the Bahamas, Yucatan, and the often blocked by spillways, are steep Caribbean. Texas and northern Mexico sided and generally do not have pupfish populations of the "variegatus complex" habitat and do not, as far as known, sup­ have been delineated by Echelle and port pupfish populations. Cyprinodon Echelle (1978), Echelle and Miller (1974) and hubbsi prefers open sandy areas, often Miller and Echelle (1975), but elec­ with a light silt cover, in very shallow lit­ trophoretic techniques have not been toral zones often including nearby patches employed. In addition, Cyprinodon popula­ of emergent vegetation. We have also tions in several central Florida freshwater found that C. hubbsi (and C. variegatus) lakes have either been designated as C. will aggregate on hard, algal covered hubbsi or C. v. hubbsi by various authors substrates of boat ramps. Although (Carr, 1936; Johnson and Snelson, 1978; Cyprinodon variegatus occurs in some Humphries and Miller, 1981). areas of the St. Johns River, the species Cyprinodon variegatus and its related has not been collected, despite intensive forms are euryhaline (Simpson and Gunter, surveys, from the Ocklawaha. 1956; Martin, 1968). We have collected C. Carr (1936) delineated C. hubbsi from variegatus on Big Pine Key, Florida, from C. variegatus on the basis of several mor­ salinities of 5 ppt and 63 ppt on the same phometric and meristic features. Since day at localities approximately 2 km apart. that publication, Johnson and Snelson's We also collected the species at the (1978) brief report using morphological northern end of Key Largo in a hypersaline data, based in part on Johnson's un­ lagoon at 81 ppt. Nearby, on the southern published Master's thesis, Univ. of Central end of the Florida peninsula from Lake Florida, remains the only recent taxonomic Okeechobee southward through the analysis of C. hubbsi and its relationship Everglades, C. variegatus occurs in fresh to C. variegatus. Johnson and Snelson's or brackish waters (Ager, 1971; Kushlan (1978) report is important as it includes and Lodge, 1974). Miller (1948) suggested several populations of the nominal C. a positive correlation between meristic hubbsi and demonstrates more of the ex­ features and salinity, but did not apply isting morphological variation within that rigorous statistical tests to his data, for form than Carr's (1936) original description. desert pupfishes in the western United Johnson and Snelson (1978) concluded States. Our electrophoretic data, and the that C. hubbsi should be relegated to the meristic data of Johnson and Snelson synonymy of C. variegatus. (1978), do not indicate such a correlation We present electrophoretic data for for Florida Cyprinodon. This is an impor­ Lakes Eustis, Dora, Weir, Harris and Grif­ tant point since the nominal C. hubbsi, fin, all "hubbsi" lakes. Lake Weir is the https://aquila.usm.edu/goms/vol6/iss2/3 2 DOI: 10.18785/negs.0602.03 Duggins et al.: Electrophoretic Comparison of Cyprinodon variegatus Lacépède and Electrophoretic comparison of Cyprinodon 101 most isolate.d geographically of these. placed on a block of dry ice until returned The purpose of this paper is to pre­ to the laboratory. In the field, salinity was sent data from our investigations on two recorded with an American Optical In­ aspects of the problem of speciation in the struments refractometer. Twenty genus Cyprinodon: specimens were used for electrophoresis 1. genetic variability in Cyprinodon from each locality (Figure 1). All collections variegatus in Florida. were made in May, 1981 except where 2. the relationship of nominal Cyprin­ noted. odon hubbsi populations to one Cyprinodon variegatus: Florida: another and to C. variegatus. (population number 1) Brevard Co., Cocoa Our analysis should provide insights Beach, Dec. 1980, salinity not recorded; (2) into speciation in the genus Cyprinodon Indian River Co., Long Point Co. Park, and establish a foundation for examination 16 °/00; (3) Indian River Co., Sebastian Inlet, by electrophoretic methods of allopatric 36 °/00; (4) St. Johns Co., Anastasia St. Park, populations in Texas freshwaters, northern 32 °/00; (5) Monroe Co., Key Largo, 81 °/00; (6) Mexico, Yucatan, the Bahamas and on Monroe Co., Grassy Key, 60 °/00, (7) Monroe Caribbean Islands. Co., Big Pine Key, 63 °/00; (8) Hillsborough Co., Alafia River @ Rte. 41, 34 °/00 ; (9) MATERIALS AND METHODS Manatee Co., Causeway to Anna Maria Beach (Rte. 64), 36 °/00; (10) Wakulla Co., Collections were made with a 4.6 pond at St. Marks Lighthouse, 16 °/00; (11) meter (7mm mesh) seine. The fishes were Wakulla Co., Gulf coast at Panacea, 37 °/00; placed in a Zip-Loc bag, covered with the (12) Wakulla Co., Panacea, tidal creek, Dec. water in which they were collected, and 1980, salinity not recorded. Cyprinodon hubbsi: Florida: (13) Lake Co., Lake Harris at Leesburg; (14) Lake Co., Lake Dora at Mt. Dora; (15) Marion Co., Lake Weir at Oklawaha; (16) Lake Co., Lake Griffin at Coca Cola Park, on east side of lake; (17) Lake Co., Lake Eustis at Eustis. Salinity 0°/00 at all C. hubbsi localities. To obtain protein samples for elec­ trophoresis, individual fish were homogenized in an equal volume of chill­ ed distilled water; the slurry that resulted was centrifuged at 25,000g at 4 °C for 60 min. The supernatant of water soluble pro­ teins was decanted and stored at 4 oc over­ night, a maximum of 18 hrs. prior to elec­ trophoretic separations. The 20 loci coding for proteins surveyed in this study were: nonenzymatic proteins (Gp-1, 2, 3, 4, 5); esterases (Est-1, 2, 3, 4); glucosephosphate isomerases (Gpi-A, B); glycerol-3- Figure 1.
Recommended publications
  • Monitoring and Understanding Toxic Cyanobacteria and Cochlodinium Polykrikoides Blooms in Suffolk County
    MONITORING AND UNDERSTANDING TOXIC CYANOBACTERIA AND COCHLODINIUM POLYKRIKOIDES BLOOMS IN SUFFOLK COUNTY A FINAL REPORT BY CHRISTOPHER J. GOBLER, STONY BROOK UNIVERSITY SUBMITTED SEPTEMBER 2013 REVISED MAY 2014 1 TABLE OF CONTENTS: Executive Summary……………………………………………………………pages 3- 6 Task 1. – Literature and Regulatory Review…………………………………pages 7 - 14 Task 2. –Summer monitoring of freshwater bathing beach lakes in Suffolk County. Suffolk County Bathing Beaches………………………………….…………pages 15 - 16 Task 3. Seasonal monitoring the most toxic lakes in Suffolk County…..……pages 17 - 25 Task 4. Cyanotoxin findings and final report………………………...…………..pages 26 Task 5 & 6. Assess the ability of Cochlodinium polykrikoides to form cysts; Quantify the production and densities of Cochlodinium polykrikoides cysts before, during and after blooms………………………………………………………………..………pages 27 - 57 Task 7. Assess the temperature tolerance of Cochlodinium polykrikoides….pages 58 - 61 Task 8. Assess the mechanism of toxicity of Cochlodinium polykrikoides....pages 62 - 93 Task 9. Explore the vulnerability of Suffolk County fish populations to Cochlodinium polykrikoides………………………………………………………...………pages 94 - 113 Task 10. Prepare a final report regarding Cochlodinium polykrikoides results….pages 114 2 EXECUTIVE SUMMARY This project, Monitoring and Understanding Toxic Cyanobacteria and Cochlodinium polykrikoides Blooms in Suffolk County, was funded by Suffolk County Capital Project 8224, Harmful Algal Blooms, and was initiated to address ongoing blooms of toxic cyanobacteria and Cochlodinium polykrikoides in Suffolk County waters. Cyanobacteria Cyanobacteria, also known as blue-green algae, are microscopic organisms found in both marine and fresh water environments. Under favorable conditions of sunlight, temperature, and nutrient concentrations, cyanobacteria can form massive blooms that discolor the water and often result in a scums and floating mats on the water’s surface.
    [Show full text]
  • Relation of Desert Pupfish Abundance to Selected Environmental Variables
    Environmental Biology of Fishes (2005) 73: 97–107 Ó Springer 2005 Relation of desert pupfish abundance to selected environmental variables in natural and manmade habitats in the Salton Sea basin Barbara A. Martin & Michael K. Saiki U.S. Geological Survey, Biological Resources Division, Western Fisheries Research Center-Dixon Duty Station, 6924 Tremont Road, Dixon, CA 95620, U.S.A. (e-mail: [email protected]) Received 6 April 2004 Accepted 12 October 2004 Key words: species assemblages, predation, water quality, habitat requirements, ecological interactions, endangered species Synopsis We assessed the relation between abundance of desert pupfish, Cyprinodon macularius, and selected biological and physicochemical variables in natural and manmade habitats within the Salton Sea Basin. Field sampling in a natural tributary, Salt Creek, and three agricultural drains captured eight species including pupfish (1.1% of the total catch), the only native species encountered. According to Bray– Curtis resemblance functions, fish species assemblages differed mostly between Salt Creek and the drains (i.e., the three drains had relatively similar species assemblages). Pupfish numbers and environmental variables varied among sites and sample periods. Canonical correlation showed that pupfish abundance was positively correlated with abundance of western mosquitofish, Gambusia affinis, and negatively correlated with abundance of porthole livebearers, Poeciliopsis gracilis, tilapias (Sarotherodon mossambica and Tilapia zillii), longjaw mudsuckers, Gillichthys mirabilis, and mollies (Poecilia latipinna and Poecilia mexicana). In addition, pupfish abundance was positively correlated with cover, pH, and salinity, and negatively correlated with sediment factor (a measure of sediment grain size) and dissolved oxygen. Pupfish abundance was generally highest in habitats where water quality extremes (especially high pH and salinity, and low dissolved oxygen) seemingly limited the occurrence of nonnative fishes.
    [Show full text]
  • Three New Pupfish Species, Cyprinodon (Teleostei, Cyprinodontidae), from Chihuahua, México, and Arizona, USA Author(S): W
    Three New Pupfish Species, Cyprinodon (Teleostei, Cyprinodontidae), from Chihuahua, México, and Arizona, USA Author(s): W. L. Minckley, Robert Rush Miller and Steven Mark Norris Source: Copeia, Vol. 2002, No. 3 (Aug. 15, 2002), pp. 687-705 Published by: American Society of Ichthyologists and Herpetologists (ASIH) Stable URL: http://www.jstor.org/stable/1448150 . Accessed: 23/07/2014 15:57 Your use of the JSTOR archive indicates your acceptance of the Terms & Conditions of Use, available at . http://www.jstor.org/page/info/about/policies/terms.jsp . JSTOR is a not-for-profit service that helps scholars, researchers, and students discover, use, and build upon a wide range of content in a trusted digital archive. We use information technology and tools to increase productivity and facilitate new forms of scholarship. For more information about JSTOR, please contact [email protected]. American Society of Ichthyologists and Herpetologists (ASIH) is collaborating with JSTOR to digitize, preserve and extend access to Copeia. http://www.jstor.org This content downloaded from 128.123.44.23 on Wed, 23 Jul 2014 15:57:21 PM All use subject to JSTOR Terms and Conditions Copeia,2002(3), pp. 687-705 Three New Pupfish Species, Cyprinodon(Teleostei, Cyprinodontidae), from Chihuahua, Mexico, and Arizona, USA W. L. MINCKLEY,ROBERT RUSH MILLER,AND STEVENMARK NORRIS Three new species of Cyprinodon(Teleostei, Cyprinodontidae)are described,each long recognized as distinct. Cyprinodonpisteri occupies a varietyof systems and hab- itats in the Lago de Guzmin complex basin in northern Chihuahua,Mexico. It is distinguishedby its dusky to black dorsal fin and narrowor inconspicuousterminal bar on the caudal fin in mature males.
    [Show full text]
  • Distribution of Amargosa River Pupfish (Cyprinodon Nevadensis Amargosae) in Death Valley National Park, CA
    California Fish and Game 103(3): 91-95; 2017 Distribution of Amargosa River pupfish (Cyprinodon nevadensis amargosae) in Death Valley National Park, CA KRISTEN G. HUMPHREY, JAMIE B. LEAVITT, WESLEY J. GOLDSMITH, BRIAN R. KESNER, AND PAUL C. MARSH* Native Fish Lab at Marsh & Associates, LLC, 5016 South Ash Avenue, Suite 108, Tempe, AZ 85282, USA (KGH, JBL, WJG, BRK, PCM). *correspondent: [email protected] Key words: Amargosa River pupfish, Death Valley National Park, distribution, endangered species, monitoring, intermittent streams, range ________________________________________________________________________ Amargosa River pupfish (Cyprinodon nevadensis amargosae), is one of six rec- ognized subspecies of Amargosa pupfish (Miller 1948) and survives in waters embedded in a uniquely harsh environment, the arid and hot Mojave Desert (Jaeger 1957). All are endemic to the Amargosa River basin of southern California and Nevada (Moyle 2002). Differing from other spring-dwelling subspecies of Amargosa pupfish (Cyprinodon ne- vadensis), Amargosa River pupfish is riverine and the most widely distributed, the extent of which has been underrepresented prior to this study (Moyle et al. 2015). Originating on Pahute Mesa, Nye County, Nevada, the Amargosa River flows intermittently, often under- ground, south past the towns of Beatty, Shoshone, and Tecopa and through the Amargosa River Canyon before turning north into Death Valley National Park and terminating at Badwater Basin (Figure 1). Amargosa River pupfish is data deficient with a distribution range that is largely unknown. The species has been documented in Tecopa Bore near Tecopa, Inyo County, CA (Naiman 1976) and in the Amargosa River Canyon, Inyo and San Bernardino Counties, CA (Williams-Deacon et al.
    [Show full text]
  • Compare and Contrast the Water Environment Between Death Valley Pupfish Specie and Devil’S Hole Pupfish Specie
    Compare and Contrast the Water environment between Death Valley Pupfish Specie and Devil’s Hole Pupfish Specie By Roy Tianran Gao 1 Table of Contents Title page 1 Abstract 3 Introduction and Background 3 Water Temperature 4 Salinity 6 Water Level 7 Conservation 10 Conclusion 11 References 12 2 ABSTRACT The two types of pupfish (Cyprinodon) in Death Valley National Park are Death Valley pupfish and Devil’s Hole pupfish. Death Valley pupfish has been existed over 10,000 years and Devil’s Hole pupfish has been existed for over 20,000 years. Both of the pupfishes are endangered species. The average number of Death Valley pupfish has decreased by about 100 since 1990s, and the number of Devil’s Hole pupfish has decreased by 400 since 1995. Comparing the water level, water temperature and the water salinity between the two species of pupfish would help to define the living requirements and reason of decreasing population. The research toward the result is based on 7 journal articles, 4 websites, and 1 book. As the result shows, Death Valley Pupfish and Devil’s Hole Pupfish live in different water environments and functioned differently. Understanding the water environment of the two types of pupfishes will help people building new habitats for pupfishes and increase their population so that would be possible to avoid the extinction of pupfishes from the earth. INTRODUCTION AND BACKGROUND Pupfish is a small killifish in the Southwest of America. There are five pupfish species in Death Valley which are Armargosa pupfish, Saratoga Pupfish, Devil’s Hole pupfish, Death Valley pupfish, and Cotton ball Marsh pupfish (National Park Service, 2008).
    [Show full text]
  • Facilitating Foundation Species: the Potential for Plant–Bivalve Interactions to Improve Habitat Restoration Success
    Received: 28 March 2019 | Accepted: 3 February 2020 DOI: 10.1111/1365-2664.13605 REVIEW Facilitating foundation species: The potential for plant–bivalve interactions to improve habitat restoration success Karine Gagnon1 | Eli Rinde2 | Elizabeth G. T. Bengil3,4 | Laura Carugati5 | Marjolijn J. A. Christianen6,7 | Roberto Danovaro5,8 | Cristina Gambi5 | Laura L. Govers7,9 | Silvija Kipson10 | Lukas Meysick1 | Liina Pajusalu11 | İnci Tüney Kızılkaya3,12 | Johan van de Koppel9,13 | Tjisse van der Heide7,9,14 | Marieke M. van Katwijk7 | Christoffer Boström1 1Environmental and Marine Biology, Åbo Akademi University, Turku, Finland; 2Norwegian Institute for Water Research, Oslo, Norway; 3Mediterranean Conservation Society, Izmir, Turkey; 4Girne American University, Marine School, Girne, TRNC via Turkey; 5Department of Life and Environmental Sciences, Polytechnic University of Marche, Ancona, Italy; 6Aquatic Ecology and Water Quality Management Group, Wageningen University, Wageningen, The Netherlands; 7Department of Environmental Science, Institute for Wetland and Water Research, Radboud University Nijmegen, Nijmegen, The Netherlands; 8Stazione Zoologica Anton Dohrn, Naples, Italy; 9Groningen Institute for Evolutionary Life Sciences, University of Groningen, Groningen, The Netherlands; 10Faculty of Science, Department of Biology, University of Zagreb, Zagreb, Croatia; 11Estonian Marine Institute, University of Tartu, Tallinn, Estonia; 12Faculty of Science, Ege University, Izmir, Turkey; 13Royal Netherlands Institute for Sea Research and Utrecht
    [Show full text]
  • An Updated List of Taxonomy, Distribution and Conservation Status (Teleostei: Cyprinodontoidea)
    Iran. J. Ichthyol. (March 2018), 5(1): 1–29 Received: January 5, 2018 © 2018 Iranian Society of Ichthyology Accepted: March 1, 2018 P-ISSN: 2383-1561; E-ISSN: 2383-0964 doi: 10.22034/iji.v5i1.267 http://www.ijichthyol.org Review Article Cyprinodontid fishes of the world: an updated list of taxonomy, distribution and conservation status (Teleostei: Cyprinodontoidea) Hamid Reza ESMAEILI1*, Tayebeh ASRAR1, Ali GHOLAMIFARD2 1Ichthyology and Molecular Systematics Research Laboratory, Zoology Section, Department of Biology, College of Sciences, Shiraz University, Shiraz, Iran. 2Department of Biology, Faculty of Sciences, Lorestan University, 6815144316 Khorramabad, Iran. Email: [email protected] Abstract: This checklist aims to list all the reported cyprinodontid fishes (superfamily Cyprinodontoidea/pupfishes) of the world. It lists 141 species in 8 genera and 4 families. The most diverse family is Cyprinodontidae (54 species, 38%), followed by Orestiidae (45 species, 32%), Aphaniidae (39 species, 28%), and Cubanichthyidae (3 species, 2%). Among 141 listed species, 73 (51.8%) species are Not Evaluated (NE), 15 (10.6%) Least Concern (LC), 9 (6.4%) Vulnerable (VU), 3 (2.1%) Data Deficient (DD), 11 (7.8%) Critically Endangered (CR), 4 (2.8%) Near Threatened (NT), 18 (12.8%) Endangered (EN), 3 (2.1%) Extinct in the Wild (EW) and 5 (3.5%) Extinct of the Red List of IUCN. They inhabit in the fresh, brackish and marine waters of the United States, Middle America, the West Indies, parts of northern South America, North Africa, the Mediterranean Anatolian region, coastal areas of the Persian Gulf and Makran Sea (Oman Sea), the northern Arabian Sea east to Gujarat in India, and some endorheic basins of Iran, Pakistan and the Arabian Peninsula.
    [Show full text]
  • Four New Pupfishes of the Genus Cyprinodon from Mexico, with a Key to the C
    FOUR NEW PUPFISHES OF THE GENUS CYPRINODON FROM MEXICO, WITH A KEY TO THE C. EXIMIUS COMPLEX ROBERT RUSH MILLER Reprinted from BULLETIN OF THE SOUTHERN CALIFORNIA ACADEMY OF SCIENCES Vol. 75, No. 2, August 1976 pp. 68-75 Made in tile United States of America FOUR NEW PUPFISHES OF THE GENUS CYPRINODON FROM MEXICO, WITH A KEY TO THE C. EXIMIUS COMPLEX ROBERT RUSH MILLER' ABSTRACT: The pupfishes (genus Cyprinodon) referable to the C. eximius complex comprise seven species that are restricted to, or had their origin in, the Chihuahuan Desert region of Mexico and adjacent parts of Texas and New Mexico. Four are described as new; the remainder are C. eximius, C. atrorus, and C. latifasciatus. Most are of restricted distribution; one is extinct and another may be. Keys, diagnoses, and ranges are given for each species and all are illustrated. The distinctive morphometric characters of the new species are given. Life colors and color patterns are important in distinguishing species. More than fifty years ago, while on the staff of elongated, the pelvic length entering mandible the Field Museum of Natural History, Carl L. length less than 1.0 times - - - - - - - - - - - - - 3 Hubbs began to gather data for an intended 3. a. Caudal fin of nuptial male with prominent revision of the genus Cyprinodon (Hubbs, 1926: black spots or dashes on interradial membranes 2 17). He subsequently described the distinctive of basal 1/2 to 4-1 of fin, usually irregularly arranged but sometimes aligned in about Yucatan pupfish, C. variegatus artifrons (Hubbs, 3 vertical rows; terminal black bar immediately 1936: 223-225, pl.
    [Show full text]
  • Desert Fish: Life on the Edge
    Desert Fish: by Linus Chen Life on the Edge Ash Meadows speckled dace Photo by John & Karen Hollingsworth/USFWS smallest at 3/4 inch (1.9 cm), is the only pupfish not to show aggressive territorial behavior.) During the year-round breeding season, the more colorful and deeper-bodied males of most pupfish taxa will pursue females into an area with fine sand, silt, and perhaps algae. After an elaborate courtship display by the male pupfish, the female deposits one or two eggs, which the male immediately fertilizes. Large female pupfish can lay about 25 eggs per day and may spawn with different males Fairbanks Springs, a small oasis in A few miles away, in Scruggs, Indian, each day. The eggs may be protected by the Nevada desert, resembles a large hot Marsh, and School springs, lives the the territorial behavior of males, but in tub from the bottom of which someone Warm Springs Amargosa pupfish (C. n. general there is no parental care of the forgot to scrub the algae. Fortunately, pectoralis). The Ash Meadows speckled eggs. In warmer springs, pupfish can algae thrive in this spring pool, for they dace (Rhinichthys osculus nevadensis) reach sexual maturity at 2 to 4 months, are integral to the life cycle of the Ash may still be found at Jack Rabbit and and live for 6 to 9 months after reaching Meadows Amargosa pupfish Bradford springs, and the only natural the free swimming stage. Pupfish living (Cyprinodon nevadensis mionectes). population of the Devils Hole pupfish in cooler waters grow more slowly, but The subspecies name “mionectes” is (C.
    [Show full text]
  • Population Ecology and Monitoring of the Endangered Devils Hole Pupfish Maria Dzul Iowa State University
    View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Digital Repository @ Iowa State University Iowa State University Capstones, Theses and Graduate Theses and Dissertations Dissertations 2011 Population ecology and monitoring of the endangered Devils Hole pupfish Maria Dzul Iowa State University Follow this and additional works at: https://lib.dr.iastate.edu/etd Part of the Environmental Sciences Commons Recommended Citation Dzul, Maria, "Population ecology and monitoring of the endangered Devils Hole pupfish" (2011). Graduate Theses and Dissertations. 10278. https://lib.dr.iastate.edu/etd/10278 This Thesis is brought to you for free and open access by the Iowa State University Capstones, Theses and Dissertations at Iowa State University Digital Repository. It has been accepted for inclusion in Graduate Theses and Dissertations by an authorized administrator of Iowa State University Digital Repository. For more information, please contact [email protected]. Population ecology and monitoring of the endangered Devils Hole pupfish by Maria Christina Dzul A thesis submitted to the graduate faculty in partial fulfillment of the requirements for the degree of MASTER OF SCIENCE Major: Wildlife Ecology Program of Study Committee: Stephen J. Dinsmore, Co-Major Professor Michael C. Quist, Co-Major Professor Philip M. Dixon Iowa State University Ames, Iowa 2011 ii TABLE OF CONTENTS LIST OF TABLES iv LIST OF FIGURES vi ACKNOWLEDGEMENTS xi CHAPTER 1. GENERAL INTRODUCTION 1 Thesis Organization 5 References 6 CHAPTER 2. IDENTIFYING SOURCES OF ERROR IN SURVEYS OF ADULT DEVILS HOLE PUPFISH 9 Abstract 9 Introduction 10 Methods 12 Results 16 Discussion 18 References 23 Tables 27 Figures 28 CHAPTER 3.USING VARIANCE COMPONENTS TO ESTIMATE POWER IN A HIERARCHICALLY NESTED SAMPLING DESIGN: IMPROVING MONITORING OF LARVAL DEVILS HOLE PUPFISH 30 Abstract 30 Introduction 31 Methods 34 Study Area 34 Survey Design 35 Statistical Analysis 36 Results 39 Discussion 40 Conclusion 44 References 47 Tables 52 Figures 53 iii CHAPTER 4.
    [Show full text]
  • Lake Apopka a Decade of Improvement Now Accelerating
    Lake Apopka A decade of improvement now accelerating Location Downstream to the north, the pollution spread FAST FACTS Located in northwest Orange and southeast throughout the Ocklawaha Chain of Lakes. Lake Lake counties, Lake Apopka is the headwaters Beauclair received 85 percent of its phosphorus of the Ocklawaha Chain of Lakes. pollution from Lake Apopka. In Lakes Dora and Once a world-class Eustis, the numbers were 65 percent and 24 bass fishery, 50 Fed by a natural spring, rainfall and stormwater percent, respectively. To protect the Ocklawaha runoff, water from Lake Apopka flows through Chain, the flow of pollutants from Lake Apopka years of abuse the Apopka-Beauclair Canal and into Lakes had to be stemmed. tagged Lake Beauclair and Dora. From Lake Dora, water Apopka with the flows into Lake Eustis, then into Lake Griffin The restoration of Lake Apopka infamous title of and then northward into the Ocklawaha River, The Lake Apopka Restoration Act of 1985 and which flows into the St. Johns River. Florida’s most Florida’s Surface Water Improvement and Management (SWIM) Act in 1987 paved the way polluted large lake. Through the 1940s, Lake Apopka was one of for restoration work to begin. central Florida’s main attractions. Anglers In response to the traveled from throughout the United States to The primary goals for the restoration of the fish for trophy-sized bass in Lake Apopka, and District’s efforts, lake’s ecosystem are to 21 fish camps lined the lake’s shoreline. • Reduce the amount of phosphorus going into water quality has Lake Apopka improved for more The lake’s decline • Remove phosphorus and other suspended than a decade.
    [Show full text]
  • Upper Ocklawaha Basin Management Action Plan ______10 AP.4
    Final – August 14, 2007 BASIN MANAGEMENT ACTION PLAN For the Implementation of Total Maximum Daily Loads Adopted by the Florida Department of Environmental Protection in the UPPER OCKLAWAHA RIVER BASIN Developed by the Upper Ocklawaha Basin Working Group in Cooperation with the Florida Department of Environmental Protection Division of Water Resource Management Bureau of Watershed Management August 14, 2007 ii Final – August 14, 2007 TABLE OF CONTENTS Acknowledgments ___________________________________________________ viii List of Acronyms _____________________________________________________ ix I. ADOPTED UPPER OCKLAWAHA RIVER BASIN MANAGEMENT ACTION PLAN ________________________ 1 Upper Ocklawaha River Basin Working Group Members and Other Participants _____________________________________________________ 2 2007 Upper Ocklawaha River Basin Management Action Plan Addressing the 2003 TMDLs__________________________________________________ 4 AP.1. Background _________________________________________________________4 AP.2. Total Maximum Daily Loads ____________________________________________5 AP.3. BMAP Process ______________________________________________________8 AP.3.1. Allocations _______________________________________________________ 10 AP.3.2. Upper Ocklawaha Basin Management Action Plan ________________________ 10 AP.4. Monitoring Program__________________________________________________22 AP.5. Tracking and Follow-up Actions ________________________________________23 AP.6. Commitment to Plan Implementation ____________________________________24
    [Show full text]