Applied Ecology and Management of a European Barbel Barbus Barbus Population of a Lowland River

Total Page:16

File Type:pdf, Size:1020Kb

Applied Ecology and Management of a European Barbel Barbus Barbus Population of a Lowland River September 2016 Applied ecology and management of a European barbel Barbus barbus population of a lowland river Tea Bašić A thesis submitted in partial fulfilment of the requirements of Bournemouth University for the degree of Doctor of Philosophy Supervisory team: Professor Robert Britton, Dr Andrew Pledger I Copyright Statement This copy of the thesis has been supplied on condition that anyone who consults it is understood to recognise that its copyright rests with the author and due acknowledgement must always be made of the use of any material contained in, or derived from, this thesis. II Abstract Freshwaters represent some of the most degraded ecosystems in the world, with approximately 56% of the European rivers being sufficiently altered by human activities to modify the composition of their biological communities. River fish communities are often used to indicate this altered status due to their ecological, recreational and economic value. In lowland rivers, habitat alterations include impoundments and activities such as channel straightening, impacting aspects of fish behaviour and lifecycle completion. Species such as European barbel B. barbus are particularly affected due to their propensity for long-distance migrations and requirements of high quality gravels for spawning. Consequently, B. barbus populations throughout Europe are increasingly threatened. Barbus barbus is indigenous to eastern flowing rivers in England, including the River Great Ouse that has been historically subjected to multiple alterations in channel morphology for flood defence and impoundments for land drainage. The river’s B. barbus population is now restricted to the upper reaches where they represent a key resource for angling, yet temporal and spatial data on their populations suggest relatively low abundances in recent years. Over the last 30 years, the regulatory authority responsible for their management (Environment Agency) have managed the population through a combination of enhancement stocking using hatchery-reared fish and habitat improvement schemes, especially gravel jetting of spawning substrates. There is, however, little knowledge on the effectiveness of these. Consequently, this research investigates B. barbus in rivers in England generally and the Great Ouse specifically by assessing the efficacy of stocking and habitat works to enhance populations. III The initial research has focused on using scales from historical surveys on the fish communities of three rivers (including the Great Ouse) to determine the trophic relationships of the fishes using stable isotope analysis. Outputs indicated that scales can be used for this analysis and revealed that rather than sharing food resources with functionally similar species such as chub Squalius cephalus, B. barbus occupied distinct isotopic (trophic) space. Their diet was then assessed using stable isotope analysis on B. barbus scales from four English rivers to determine their major food resources. Results indicated that angling heavily modified B. barbus diet, with introduced bait (as pelletized fishmeal) being the most important dietary component. The next phase of the research built of these outputs of both these studies and assessed the impact and efficacy of enhancement stocking of hatchery-reared B. barbus. In both semi-controlled and wild conditions, analyses suggested that enhancement stocking with B. barbus has minimal detrimental consequences for other fishes such as S. cephalus, with strong patterns of trophic niche partitioning. Nevertheless, the efficacy of enhancement stocking might be limited, with low numbers of recaptured stocked B. barbus recorded in the study, with a concomitant genetic study revealing negligible introgression of stocked B. barbus genes into the population, despite the stocking activities. Given that enhancement stocking has been of limited success to improve B. barbus population abundance in the Great Ouse catchment, their spawning habitats were assessed in the river, including whether the physicochemical properties of the sediments and hyporhic water were limiting. Whilst results indicated good quality of hyporehic water, the subsurface sediment was high in fine content, particularly sand. Gravel jetting, a method to clear spawning gravels of fine content, was shown to only provide short term benefits (e.g. 3 months) in reducing this content of fines, with this benefit only apparent in surface sediments and not in the subsurface. An ex-situ experiment to IV assess the tolerance of B. barbus eggs and larvae to sand content in spawning substrata indicated no effect of high sand content on egg to emergence survival rates, but it did significantly decrease the timing of larval emergence from gravels. This early emergence of B. barbus larvae from substrates with high sand content could potentially impact their subsequent survival in the wild. Thus, the current management strategies employed in the River Great Ouse to enhance the B. barbus populations appear to have limited success, largely failing to meet their objectives. Thus, more holistic management approaches are outlined and suggested for implementation. V Table of contents Abstract .................................................................................................................................... iii Table of contents ....................................................................................................................... vi List of Figures ........................................................................................................................... ix List of Tables ........................................................................................................................... xv Acknowledgements ................................................................................................................. xix Author’s declaration ................................................................................................................. xx 1. Introduction .......................................................................................................................... 1 1.1 Lowland rivers and their anthropogenic modification ..................................................... 1 1.2 Measuring the impact of anthropogenic alterations on lowland rivers ............................ 1 1.3 Stable isotope analysis as a tool for measuring long-term change ................................... 3 1.4 Focal fish species and river system .................................................................................. 6 1.5 Mitigation strategies to enhance river fish communities ................................................ 11 1.5.1 Fish stocking.......................................................................................................... 11 1.5.2 Habitat restoration ................................................................................................. 15 1.6 Research aims and objectives ......................................................................................... 21 1.7 Thesis structure............................................................................................................... 23 2. Utility of fish scales from stock assessment surveys in stable isotope analysis for initial assessments of trophic relationships in riverine fishes ............................................ 24 2.1 Summary ........................................................................................................................ 25 2.2 Introduction .................................................................................................................... 26 2.3 Materials and methods.................................................................................................... 27 2.4 Results ............................................................................................................................ 29 2.5 Discussion ...................................................................................................................... 36 3. Diet composition of Barbus barbus in four rivers in England: importance of angling baits and invasive crayfish as trophic subsidies .................................................... 39 3.1 Summary ........................................................................................................................ 40 3.2 Introduction .................................................................................................................... 41 3.3 Materials and methods.................................................................................................... 43 3.4 Results ............................................................................................................................ 46 3.5 Discussion ...................................................................................................................... 52 4. Trophic ecology of stocked European barbel Barbus barbus and resident cyprinid fishes: consistency in niche partitioning over time, space and body sizes ......... 57 4.1 Summary ........................................................................................................................ 58 4.2 Introduction .................................................................................................................... 59 4.3 Materials and methods.................................................................................................... 62 4.3.1 Pond mesocosm
Recommended publications
  • BONY FISHES 602 Bony Fishes
    click for previous page BONY FISHES 602 Bony Fishes GENERAL REMARKS by K.E. Carpenter, Old Dominion University, Virginia, USA ony fishes constitute the bulk, by far, of both the diversity and total landings of marine organisms encoun- Btered in fisheries of the Western Central Atlantic.They are found in all macrofaunal marine and estuarine habitats and exhibit a lavish array of adaptations to these environments. This extreme diversity of form and taxa presents an exceptional challenge for identification. There are 30 orders and 269 families of bony fishes presented in this guide, representing all families known from the area. Each order and family presents a unique suite of taxonomic problems and relevant characters. The purpose of this preliminary section on technical terms and guide to orders and families is to serve as an introduction and initial identification guide to this taxonomic diversity. It should also serve as a general reference for those features most commonly used in identification of bony fishes throughout the remaining volumes. However, I cannot begin to introduce the many facets of fish biology relevant to understanding the diversity of fishes in a few pages. For this, the reader is directed to one of the several general texts on fish biology such as the ones by Bond (1996), Moyle and Cech (1996), and Helfman et al.(1997) listed below. A general introduction to the fisheries of bony fishes in this region is given in the introduction to these volumes. Taxonomic details relevant to a specific family are explained under each of the appropriate family sections. The classification of bony fishes continues to transform as our knowledge of their evolutionary relationships improves.
    [Show full text]
  • §4-71-6.5 LIST of CONDITIONALLY APPROVED ANIMALS November
    §4-71-6.5 LIST OF CONDITIONALLY APPROVED ANIMALS November 28, 2006 SCIENTIFIC NAME COMMON NAME INVERTEBRATES PHYLUM Annelida CLASS Oligochaeta ORDER Plesiopora FAMILY Tubificidae Tubifex (all species in genus) worm, tubifex PHYLUM Arthropoda CLASS Crustacea ORDER Anostraca FAMILY Artemiidae Artemia (all species in genus) shrimp, brine ORDER Cladocera FAMILY Daphnidae Daphnia (all species in genus) flea, water ORDER Decapoda FAMILY Atelecyclidae Erimacrus isenbeckii crab, horsehair FAMILY Cancridae Cancer antennarius crab, California rock Cancer anthonyi crab, yellowstone Cancer borealis crab, Jonah Cancer magister crab, dungeness Cancer productus crab, rock (red) FAMILY Geryonidae Geryon affinis crab, golden FAMILY Lithodidae Paralithodes camtschatica crab, Alaskan king FAMILY Majidae Chionocetes bairdi crab, snow Chionocetes opilio crab, snow 1 CONDITIONAL ANIMAL LIST §4-71-6.5 SCIENTIFIC NAME COMMON NAME Chionocetes tanneri crab, snow FAMILY Nephropidae Homarus (all species in genus) lobster, true FAMILY Palaemonidae Macrobrachium lar shrimp, freshwater Macrobrachium rosenbergi prawn, giant long-legged FAMILY Palinuridae Jasus (all species in genus) crayfish, saltwater; lobster Panulirus argus lobster, Atlantic spiny Panulirus longipes femoristriga crayfish, saltwater Panulirus pencillatus lobster, spiny FAMILY Portunidae Callinectes sapidus crab, blue Scylla serrata crab, Samoan; serrate, swimming FAMILY Raninidae Ranina ranina crab, spanner; red frog, Hawaiian CLASS Insecta ORDER Coleoptera FAMILY Tenebrionidae Tenebrio molitor mealworm,
    [Show full text]
  • Comparison of the Myxobolus Fauna of Common Barbel from Hungary and Iberian Barbel from Portugal
    Vol. 100: 231–248, 2012 DISEASES OF AQUATIC ORGANISMS Published September 12 doi: 10.3354/dao02469 Dis Aquat Org Comparison of the Myxobolus fauna of common barbel from Hungary and Iberian barbel from Portugal K. Molnár1,*, E. Eszterbauer1, Sz. Marton1, Cs. Székely1, J. C. Eiras2 1Institute for Veterinary Medical Research, Centre for Agricultural Research, HAS, POB 18, 1581 Budapest, Hungary 2Departamento de Biologia, e CIIMAR, Faculdade de Ciências, Universidade do Porto, Rua do Campo Alegre, s/n, Edifício FC4, 4169-007 Porto, Portugal ABSTRACT: We compared Myxobolus infection of common barbel Barbus barbus from the Danube River in Hungary with that in Iberian barbel Luciobarbus bocagei from the Este River in Portugal. In Hungary, we recorded 5 known Myxobolus species (M. branchialis, M. caudatus, M. musculi, M. squamae, and M. tauricus) and described M. branchilateralis sp. n. In Portugal we recorded 6 Myxobolus species (M. branchialis, M. branchilateralis sp. n., M. cutanei, M. musculi, M. pfeifferi, and M. tauricus). Species found in the 2 habitats had similar spore morphology and only slight differences were observed in spore shape or measurements. All species showed a spe- cific tissue tropism and had a definite site selection. M. branchialis was recorded from the lamellae of the gills, large plasmodia of M. branchilateralis sp. n. developed at both sides of hemibranchia, M. squamae infected the scales, plasmodia of M. caudatus infected the scales and the fins, and M. tauricus were found in the fins and pin bones. In the muscle, 3 species, M. musculi, M. pfeifferi and M. tauricus were found; however they were found in distinct locations.
    [Show full text]
  • Fish Passage and Injury Risk at a Surface Bypass of a Small-Scale Hydropower Plant
    sustainability Article Fish Passage and Injury Risk at a Surface Bypass of a Small-Scale Hydropower Plant Josef Knott, Melanie Mueller, Joachim Pander and Juergen Geist * Aquatic Systems Biology Unit, Department of Ecology and Ecosystem Management, Technical University of Munich, Mühlenweg 22, 85354 Freising, Germany; [email protected] (J.K.); [email protected] (M.M.); [email protected] (J.P.) * Correspondence: [email protected]; Tel.: +49-816-171-3767 Received: 14 October 2019; Accepted: 29 October 2019; Published: 30 October 2019 Abstract: In contrast to the efforts made to develop functioning fishways for upstream migrants, the need for effective downstream migration facilities has long been underestimated. The challenge of developing well-performing bypasses for downstream migrants involves attracting the fish to the entrance and transporting them quickly and unharmed into the tailrace. In this study, the acceptance of different opening sizes of a surface bypass as well as the injuries which fish experience during the passage were examined. Overall bypass acceptance was low compared to the turbine passage. There was no significant difference in the number of downstream moving fish between the small and the large bypass openings. Across all fish species, no immediate mortality was detected. Severe injuries such as amputations or bruises were only rarely detected and at low intensity. Scale losses, tears and hemorrhages in the fins and dermal lesions at the body were the most common injuries, and significant species-specific differences were detected. To increase bypass efficiency, it would likely be useful to offer an alternative bottom bypass in addition to the existing surface bypass.
    [Show full text]
  • FIELD GUIDE to WARMWATER FISH DISEASES in CENTRAL and EASTERN EUROPE, the CAUCASUS and CENTRAL ASIA Cover Photographs: Courtesy of Kálmán Molnár and Csaba Székely
    SEC/C1182 (En) FAO Fisheries and Aquaculture Circular I SSN 2070-6065 FIELD GUIDE TO WARMWATER FISH DISEASES IN CENTRAL AND EASTERN EUROPE, THE CAUCASUS AND CENTRAL ASIA Cover photographs: Courtesy of Kálmán Molnár and Csaba Székely. FAO Fisheries and Aquaculture Circular No. 1182 SEC/C1182 (En) FIELD GUIDE TO WARMWATER FISH DISEASES IN CENTRAL AND EASTERN EUROPE, THE CAUCASUS AND CENTRAL ASIA By Kálmán Molnár1, Csaba Székely1 and Mária Láng2 1Institute for Veterinary Medical Research, Centre for Agricultural Research, Hungarian Academy of Sciences, Budapest, Hungary 2 National Food Chain Safety Office – Veterinary Diagnostic Directorate, Budapest, Hungary FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS Ankara, 2019 Required citation: Molnár, K., Székely, C. and Láng, M. 2019. Field guide to the control of warmwater fish diseases in Central and Eastern Europe, the Caucasus and Central Asia. FAO Fisheries and Aquaculture Circular No.1182. Ankara, FAO. 124 pp. Licence: CC BY-NC-SA 3.0 IGO The designations employed and the presentation of material in this information product do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations (FAO) concerning the legal or development status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The mention of specific companies or products of manufacturers, whether or not these have been patented, does not imply that these have been endorsed or recommended by FAO in preference to others of a similar nature that are not mentioned. The views expressed in this information product are those of the author(s) and do not necessarily reflect the views or policies of FAO.
    [Show full text]
  • FIELD GUIDE to WARMWATER FISH DISEASES in CENTRAL and EASTERN EUROPE, the CAUCASUS and CENTRAL ASIA Cover Photographs: Courtesy of Kálmán Molnár and Csaba Székely
    SEC/C1182 (En) FAO Fisheries and Aquaculture Circular I SSN 2070-6065 FIELD GUIDE TO WARMWATER FISH DISEASES IN CENTRAL AND EASTERN EUROPE, THE CAUCASUS AND CENTRAL ASIA Cover photographs: Courtesy of Kálmán Molnár and Csaba Székely. FAO Fisheries and Aquaculture Circular No. 1182 SEC/C1182 (En) FIELD GUIDE TO WARMWATER FISH DISEASES IN CENTRAL AND EASTERN EUROPE, THE CAUCASUS AND CENTRAL ASIA By Kálmán Molnár1, Csaba Székely1 and Mária Láng2 1Institute for Veterinary Medical Research, Centre for Agricultural Research, Hungarian Academy of Sciences, Budapest, Hungary 2 National Food Chain Safety Office – Veterinary Diagnostic Directorate, Budapest, Hungary FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS Ankara, 2019 Required citation: Molnár, K., Székely, C. and Láng, M. 2019. Field guide to the control of warmwater fish diseases in Central and Eastern Europe, the Caucasus and Central Asia. FAO Fisheries and Aquaculture Circular No.1182. Ankara, FAO. 124 pp. Licence: CC BY-NC-SA 3.0 IGO The designations employed and the presentation of material in this information product do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations (FAO) concerning the legal or development status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The mention of specific companies or products of manufacturers, whether or not these have been patented, does not imply that these have been endorsed or recommended by FAO in preference to others of a similar nature that are not mentioned. The views expressed in this information product are those of the author(s) and do not necessarily reflect the views or policies of FAO.
    [Show full text]
  • Order GASTEROSTEIFORMES PEGASIDAE Eurypegasus Draconis
    click for previous page 2262 Bony Fishes Order GASTEROSTEIFORMES PEGASIDAE Seamoths (seadragons) by T.W. Pietsch and W.A. Palsson iagnostic characters: Small fishes (to 18 cm total length); body depressed, completely encased in Dfused dermal plates; tail encircled by 8 to 14 laterally articulating, or fused, bony rings. Nasal bones elongate, fused, forming a rostrum; mouth inferior. Gill opening restricted to a small hole on dorsolat- eral surface behind head. Spinous dorsal fin absent; soft dorsal and anal fins each with 5 rays, placed posteriorly on body. Caudal fin with 8 unbranched rays. Pectoral fins large, wing-like, inserted horizon- tally, composed of 9 to 19 unbranched, soft or spinous-soft rays; pectoral-fin rays interconnected by broad, transparent membranes. Pelvic fins thoracic, tentacle-like,withI spine and 2 or 3 unbranched soft rays. Colour: in life highly variable, apparently capable of rapid colour change to match substrata; head and body light to dark brown, olive-brown, reddish brown, or almost black, with dorsal and lateral surfaces usually darker than ventral surface; dorsal and lateral body surface often with fine, dark brown reticulations or mottled lines, sometimes with irregular white or yellow blotches; tail rings often encircled with dark brown bands; pectoral fins with broad white outer margin and small brown spots forming irregular, longitudinal bands; unpaired fins with small brown spots in irregular rows. dorsal view lateral view Habitat, biology, and fisheries: Benthic, found on sand, gravel, shell-rubble, or muddy bottoms. Collected incidentally by seine, trawl, dredge, or shrimp nets; postlarvae have been taken at surface lights at night.
    [Show full text]
  • Download This Article in PDF Format
    Knowl. Manag. Aquat. Ecosyst. 2021, 422, 13 Knowledge & © L. Raguž et al., Published by EDP Sciences 2021 Management of Aquatic https://doi.org/10.1051/kmae/2021011 Ecosystems Journal fully supported by Office www.kmae-journal.org français de la biodiversité RESEARCH PAPER First look into the evolutionary history, phylogeographic and population genetic structure of the Danube barbel in Croatia Lucija Raguž1,*, Ivana Buj1, Zoran Marčić1, Vatroslav Veble1, Lucija Ivić1, Davor Zanella1, Sven Horvatić1, Perica Mustafić1, Marko Ćaleta2 and Marija Sabolić3 1 Department of Biology, Faculty of Science, University of Zagreb, Rooseveltov trg 6, Zagreb 10000, Croatia 2 Faculty of Teacher Education, University of Zagreb, Savska cesta 77, Zagreb 10000, Croatia 3 Institute for Environment and Nature, Ministry of Economy and Sustainable Development, Radnička cesta 80, Zagreb 10000, Croatia Received: 19 November 2020 / Accepted: 17 February 2021 Abstract – The Danube barbel, Barbus balcanicus is small rheophilic freshwater fish, belonging to the genus Barbus which includes 23 species native to Europe. In Croatian watercourses, three members of the genus Barbus are found, B. balcanicus, B. barbus and B. plebejus, each occupying a specific ecological niche. This study examined cytochrome b (cyt b), a common genetic marker used to describe the structure and origin of fish populations to perform a phylogenetic reconstruction of the Danube barbel. Two methods of phylogenetic inference were used: maximum parsimony (MP) and maximum likelihood (ML), which yielded well supported trees of similar topology. The Median joining network (MJ) was generated and corroborated to show the divergence of three lineages of Barbus balcanicus on the Balkan Peninsula: Croatian, Serbian and Macedonian lineages that separated at the beginning of the Pleistocene.
    [Show full text]
  • How Barriers Shape Freshwater Fish Distributions: a Species Distribution Model Approach
    1 How barriers shape freshwater fish distributions: a species distribution model approach 2 3 Mathias Kuemmerlen1* [email protected] 4 Stefan Stoll1,2 [email protected] 5 Peter Haase1,3 [email protected] 6 7 1Senckenberg Research Institute and Natural History Museum Frankfurt, Department of River 8 Ecology and Conservation, Clamecystr. 12, D-63571 Gelnhausen, Germany 9 2University of Koblenz-Landau, Institute for Environmental Sciences, Fortstr. 7, 76829 Landau, 10 Germany 11 3University of Duisburg-Essen, Faculty of Biology, Essen, Germany 12 *Corresponding author: Tel: +49 6051-61954-3120 13 Fax: +49 6051-61954-3118 14 15 Running title: How barriers shape fish distributions 16 17 Word count main text = 4679 18 1 PeerJ Preprints | https://doi.org/10.7287/peerj.preprints.2112v2 | CC BY 4.0 Open Access | rec: 18 Aug 2016, publ: 18 Aug 2016 19 Abstract 20 Aim 21 Barriers continue to be built globally despite their well-known negative effects on freshwater 22 ecosystems. Fish habitats are disturbed by barriers and the connectivity in the stream network 23 reduced. We implemented and assessed the use of barrier data, including their size and 24 magnitude, in distribution predictions for 20 species of freshwater fish to understand the 25 impacts on freshwater fish distributions. 26 27 Location 28 Central Germany 29 30 Methods 31 Obstruction metrics were calculated from barrier data in three different spatial contexts 32 relevant to fish migration and dispersal: upstream, downstream and along 10km of stream 33 network. The metrics were included in a species distribution model and compared to a model 34 without them, to reveal how barriers influence the distribution patterns of fish species.
    [Show full text]
  • Indiana Aquatic Nuisance Species (ANS) Management Plan
    Indiana Aquatic Nuisance Species (ANS) Management Plan Aruana caught by angler in Lake George, Lake County, Indiana Photo credit: Brian Breidert, IDNR Indiana Department of Natural Resources Funded by: Division of Fish and Wildlife Edited by: Phil Seng and Gwen White, D.J. Case & Associates, Mishawaka, Indiana October 1, 2003 Indiana Aquatic Nuisance Species (ANS) Management Plan Table of Contents Page Executive summary 3 Introduction 6 Why should we be concerned? 6 Why are we hearing about more nuisance exotics? 6 Are all exotic species causing problems? 7 Why do some of these species become nuisances? 7 What principles should guide invasive species management in Indiana? 8 Which species are top priorities for management in Indiana? 8 Table 1. Aquatic nuisance species on the watch list and detected 9 Nuisance fish 10 Nuisance insects and crustaceans 13 Nuisance mussels and snails 14 Diseases, pathogens and parasites 15 Aquarium pets caught from Indiana waters 17 Nuisance plants 20 Which programs are engaged in management of invasive species? 23 What regulatory authorities control management of exotic species? 29 Federal role 30 Regional role 32 State role 33 Designing an integrated comprehensive regulatory approach 33 What can Hoosiers do to prevent and control the impacts of ANS? 40 Index to the strategic management plan 41 Description of strategic management plan 44 How will we know if we succeed? 58 Literature cited 60 Glossary of terms 63 List of agency and organization acronyms 64 Appendix A. List of introduced fish and crayfish 65 Appendix B. List of invasive aquatic plants 67 Appendix C. Priority list of ANS in the Great Lakes basin 69 Appendix D.
    [Show full text]
  • Hemibarbus Labeo) Ecological Risk Screening Summary
    Barbel Steed (Hemibarbus labeo) Ecological Risk Screening Summary U.S. Fish & Wildlife Service, August 2012 Revised, February 2017 Web Version, 1/14/2018 Photo: Chinese Academy of Fishery Sciences. Licensed under CC BY-NC 3.0. Available: http://fishbase.org/photos/PicturesSummary.php?StartRow=0&ID=17301&what=species&TotRe c=9. (February 2017). 1 Native Range and Status in the United States Native Range From Froese and Pauly (2016): “Asia: throughout the Amur basin [Berg 1964]; eastern Asia from the Amur basin to northern Vietnam, Japan and islands of Hainan and Taiwan [Reshetnikov et al. 1997].” Status in the United States This species has not been reported in the United States. 1 Means of Introductions in the United States This species has not been reported in the United States. Remarks From CABI (2017): “Other Scientific Names Acanthogobio oxyrhynchus Nikolskii, 1903 Barbus labeo Pallas, 1776 Barbus schlegelii Günther, 1868 Cyprinus labeo Pallas, 1776 Gobio barbus Temminck & Schlegel, 1846 Gobiobarbus labeo Pallas, 1776 Hemibarbus barbus Temminck & Schlegel, 1846 Hemibarbus longianalis Kimura, 1934 Pseudogobio chaoi Evermann & Shaw, 1927” 2 Biology and Ecology Taxonomic Hierarchy and Taxonomic Standing From ITIS (2017): “Kingdom Animalia Subkingdom Bilateria Infrakingdom Deuterostomia Phylum Chordata Subphylum Vertebrata Infraphylum Gnathostomata Superclass Osteichthyes Class Actinopterygii Subclass Neopterygii Infraclass Teleostei Superorder Ostariophysi Order Cypriniformes Superfamily Cyprinoidea Family Cyprinidae Genus Hemibarbus Bleeker, 1860 Species Hemibarbus labeo (Pallas, 1776)” “Taxonomic Status: valid” 2 Size, Weight, and Age Range From Froese and Pauly (2016): “Max length : 62.0 cm TL male/unsexed; [Novikov et al. 2002]; common length : 33.0 cm TL male/unsexed; [Berg 1964]; common length :40.6 cm TL (female); max.
    [Show full text]
  • Transposable Elements and Teleost Migratory Behaviour
    International Journal of Molecular Sciences Article Transposable Elements and Teleost Migratory Behaviour Elisa Carotti 1,†, Federica Carducci 1,†, Adriana Canapa 1, Marco Barucca 1,* , Samuele Greco 2 , Marco Gerdol 2 and Maria Assunta Biscotti 1 1 Department of Life and Environmental Sciences, Polytechnic University of Marche, Via Brecce Bianche, 60131 Ancona, Italy; [email protected] (E.C.); [email protected] (F.C.); [email protected] (A.C.); [email protected] (M.A.B.) 2 Department of Life Sciences, University of Trieste, Via L. Giorgieri, 5-34127 Trieste, Italy; [email protected] (S.G.); [email protected] (M.G.) * Correspondence: [email protected] † Equal contribution. Abstract: Transposable elements (TEs) represent a considerable fraction of eukaryotic genomes, thereby contributing to genome size, chromosomal rearrangements, and to the generation of new coding genes or regulatory elements. An increasing number of works have reported a link between the genomic abundance of TEs and the adaptation to specific environmental conditions. Diadromy represents a fascinating feature of fish, protagonists of migratory routes between marine and fresh- water for reproduction. In this work, we investigated the genomes of 24 fish species, including 15 teleosts with a migratory behaviour. The expected higher relative abundance of DNA transposons in ray-finned fish compared with the other fish groups was not confirmed by the analysis of the dataset considered. The relative contribution of different TE types in migratory ray-finned species did not show clear differences between oceanodromous and potamodromous fish. On the contrary, a remarkable relationship between migratory behaviour and the quantitative difference reported for short interspersed nuclear (retro)elements (SINEs) emerged from the comparison between anadro- mous and catadromous species, independently from their phylogenetic position.
    [Show full text]