Patterns, Determinants, and Management of Freshwater Biodiversity in Europe

Total Page:16

File Type:pdf, Size:1020Kb

Patterns, Determinants, and Management of Freshwater Biodiversity in Europe Patterns, determinants, and management of freshwater biodiversity in Europe Inaugural-Dissertation to obtain the academic degree Doctor rerum naturalium (Dr. rer. nat.) submitted to the Department of Biology, Chemistry and Pharmacy of Freie Universität Berlin by Nike Sommerwerk from Vienna, Austria 2015 Representing work from 4/2008 to 4/2013 and 4/2015 to 10/2015 Supervised by: Prof. Dr. Klement Tockner Dr. Jörg Freyhof in partnership with: Leibniz-Institute of Freshwater Ecology and Inland Fisheries (IGB), Müggelseedamm 310, 12587 Berlin, Germany. 1st Reviewer: Prof. Dr. Klement Tockner Director of the Leibniz-Institute of Freshwater Ecology and Inland Fisheries (IGB), Berlin, Germany, and Professor in Aquatic Ecology at the Department of Biology, Chemistry, and Pharmacy of the Freie Universität, Berlin, Germany. 2nd Reviewer: Prof. Dr. Daniel Hering Dean of the Faculty of Biology, Head of Aquatic Ecology Department, University of Duisburg-Essen, Essen, Germany. Date of Defense: May 12th, 2016 Contents Contents Summary ............................................................................................................................................. 1 Zusammenfassung ............................................................................................................................... 3 Introduction ......................................................................................................................................... 6 Chapter I Components and drivers of change in European freshwater fish faunas ................................................ 21 1 Abstract ........................................................................................................................................ 21 2 Introduction ................................................................................................................................... 22 3 Methods ........................................................................................................................................ 23 3.1 Dataset .................................................................................................................................. 23 3.2 Data analysis........................................................................................................................... 24 4 Results .......................................................................................................................................... 26 5 Discussion ...................................................................................................................................... 32 6 Acknowledgements ......................................................................................................................... 35 7 References ..................................................................................................................................... 35 Supporting Information A Methods ........................................................................................................................................ 39 B References ..................................................................................................................................... 40 C Results .......................................................................................................................................... 41 Chapter II Responses of the European freshwater biodiversity to anthropogenic stressors & geo-climatic drivers.. 63 1 Abstract......................................................................................................................................... 63 2 Introduction ................................................................................................................................... 64 3 Methods ........................................................................................................................................ 66 3.1 Biological data ........................................................................................................................ 66 3.2 River catchments ..................................................................................................................... 66 3.3 Anthropogenic and natural, geo-climatic descriptors ....................................................................... 67 3.4 Biodiversity metrics .................................................................................................................. 68 3.5 Data analysis........................................................................................................................... 68 4 Results .......................................................................................................................................... 69 4.1 Boosted Regression Tree Analysis (BRT) and additive effects .............................................................. 69 4.2 Generalized Linear Modelling (GLM) and interactive effects ............................................................... 71 5 Discussion ...................................................................................................................................... 73 5.1 Single anthropogenic and geo-climatic effects ............................................................................... 73 5.2 Additive anthropogenic and geo-climatic effects ............................................................................ 73 5.3 Interaction between anthropogenic and geo-climatic effects ............................................................ 74 5.4 Conclusions ............................................................................................................................ 74 6 References ..................................................................................................................................... 75 Supporting Information A Results .......................................................................................................................................... 79 i Contents Chapter III The Danube River Basin ...................................................................................................................... 82 1 Introduction ................................................................................................................................... 82 2 Historical Aspects ............................................................................................................................ 85 3 Palaeogeography and Geology ........................................................................................................... 88 4 Geomorphology .............................................................................................................................. 90 5 Climate and Hydrology ..................................................................................................................... 92 6 Biogeochemistry, Water Quality and Nutrients ........................................................................................ 94 6.1 General Characteristics ............................................................................................................. 94 6.2 Water Quality .......................................................................................................................... 94 7 Biodiversity .................................................................................................................................... 97 7.1 Riparian Vegetation .................................................................................................................. 98 7.2 Vegetated Islands .................................................................................................................... 99 7.3 Macrophytes........................................................................................................................... 99 7.4 Macroinvertebrates ................................................................................................................. 100 7.5 Fish ..................................................................................................................................... 102 7.6 Avifauna .............................................................................................................................. 105 7.7 Wetland Mammals .................................................................................................................. 106 7.8 Herpetofauna ........................................................................................................................ 107 8 Human impacts, conservation and management ................................................................................... 108 9 Major tributaries and the Danube delta ............................................................................................... 113 9.1 Inn River ............................................................................................................................... 113 9.2 Morava River.......................................................................................................................... 116 9.3 Váh River .............................................................................................................................. 118 9.4 Drava River ............................................................................................................................ 121 9.5 Tisza River ............................................................................................................................
Recommended publications
  • Chondrostoma Nasus) Ecological Risk Screening Summary
    Common Nase (Chondrostoma nasus) Ecological Risk Screening Summary U.S. Fish & Wildlife Service, April 2020 Revised, April 2020 Web Version, 2/8/2021 Organism Type: Fish Overall Risk Assessment Category: High Photo: André Karwath. Licensed under CC BY-SA 2.5. Available: https://commons.wikimedia.org/wiki/File:Chondrostoma_nasus_(aka).jpg#file. (April 2020). 1 Native Range and Status in the United States Native Range From Froese and Pauly (2021): “Europe: Basins of Black (Danube, Dniestr, South Bug and Dniepr drainages), southern Baltic (Nieman, Odra, Vistula) and southern North Seas (westward to Meuse). […] Asia: Turkey.” Status in the United States No information on occurrence, status, sale or trade in the United States was found. Chondrostoma nasus falls within Group I of New Mexico’s Department of Game and Fish Director’s Species Importation List (New Mexico Department of Game and Fish 2010). Group I species “are designated semi-domesticated animals and do not require an importation permit.” With the added restriction of “Not to be used as bait fish.” 1 Means of Introductions in the United States No introductions have been reported in the United States. Remarks Although the accepted and most used common name for Chondrostoma nasus is “Common Nase”, it appears that the simple name “Nase” is sometimes used to refer to C. nasus (Zbinden and Maier 1996; Jirsa et al. 2010). The name “Sneep” also occasionally appears in the literature (Irz et al. 2006). 2 Biology and Ecology Taxonomic Hierarchy and Taxonomic Standing From Fricke et al. (2020):
    [Show full text]
  • Fish Assemblage in the Middle Cours of the Kupa River in the Area of MHE Ilovac
    Fish assemblage in the middle cours of the Kupa river in the area of MHE Ilovac Juraj Petravić1, Matija Kresonja1, Martina Petravić2, Ratko Popović1, Milorad Mrakovčić1 1OIKON Ltd- Institute of Applied Ecology, Trg Senjskih uskoka 1-2, 10020 Zagreb, Croatia 2Ministry of Agriculture, Ulica grada Vukovara 78, 10000 Zagreb, Croatia Introduction Results and Discussion The objectives of this paper are to determine the qualitative A total of 963 individuals were caught of which 19 species from 14 and quantitative composition of the fish community, and genera, from five families Balitoridae, Cobitidae, Cyprinidae, distribution of native and non-native fishes in the area of the of Siluridae, and Centrarchidae were found. The dominant species the mini-hydroelectric power plant Ilovac on the middle cours was Chub Squalius cephalus which takes up 21.8%, followed by of the Kupa river near the dam Zaluka. The ichthyological area Spirlin Alburnoides bipunctatus with 18.4%, the least represented of the river Kupa belongs to the Danube River Basin and to the is Prussian carp Carassius gibelio with 0,2% of total number of fish NATURA 2000 ecological network. caught. During this research, three endemic fish species Danube gudgeon Gobio obtusirostris, Balkan spined loach Cobitis elongata, and Dunabe roach Rutilus virgo was recorded. Endemic species takes up 14,7% of total number of fish caught. As well as two invasive alien species (IAS) Pumpkinseed Lepomis gibbosus and Pseudorasbora Pseudorasbora parva. Non-native species in the area of MHE Ilovac hold a significant share in the fish community with 10,4 % of total number of fish caught.
    [Show full text]
  • Now Published in Limnologica 82:125765
    Demographic history, range size and habitat preferences of the groundwater amphipod Niphargus puteanus (C.L. Koch in Panzer, 1836) Dieter Weber1,2, Jean-François Flot1,3, Hannah Weigand2, Alexander M. Weigand2* 1 Université Libre de Bruxelles, Evolutionary Biology & Ecology group, Avenue F.D. Roosevelt 50, B- 1050 Brussels - Belgium 2 Musée National d'Histoire Naturelle Luxembourg, Section de zoologie, 25 Rue Münster, L-2160 Luxembourg, Luxembourg 3 Interuniversity Institute of Bioinformatics in Brussels – (IB)2, ULB-VUB, La Plaine Campus, Triomflaan, C building, 6th floor, CP 263, 1050 Brussels, Belgium *corresponding author: [email protected] Abstract Niphargus puteanus is the oldest described species of its genus and, in the past, was used as a taxonomic annotation for any subterranean amphipod record. For that reason, no clear knowledge exists about its actual range size and habitat preferences. We here applied a molecular taxonomic and phylogeographical approach based on mitochondrial and nuclear DNA to shed light on its distribution and to infer its demographic history. Furthermore, we analysed aquifer types and water flow regimes to provide a clearer picture of the species’ ecological requirements. Our results indicate that N. puteanus is widely distributed north of the Alps, having its core range in the geomorphological natural region of the ‘South German Scarplands’ (SGS). Additionally, isolated satellite populations exist in the Taunus and the Sauerland, and two single individuals were collected in Luxembourg and in Austria, respectively. The species’ maximal distribution range reaches 756 km between the two single-specimen records and 371 km within the SGS. A very high haplotype diversity was observed, revealing the presence of seven haplotype groups.
    [Show full text]
  • NEW DISTRIBUTION DATA for Alburnus Sava %RJXWVND\D =Xsdqňlň -Holî 'LULSDVNR 1DVHND $1' 7HOHVWHV VRXI°D 5LVVR
    Croatian Journal of Fisheries, 2017, 75, 137-142 M. Vucić et al.: New distribution of Alburnus sava and Telestres souffia DOI: 10.1515/cjf-2017-0017 CODEN RIBAEG ISSN 1330-061X (print), 1848-0586 (online) NEW DISTRIBUTION DATA FOR Alburnus sava %RJXWVND\D =XSDQòLò -HOLî 'LULSDVNR 1DVHND$1'7HOHVWHVVRXI°D 5LVVR ,17+(:(67(51 BALKANS Matej Vucić, Ivana Sučić, Dušan Jelić* Croatian Institute for Biodiversity, Croatian Biological Research Society, Lipovac I. 7, HR-10000 Zagreb, Croatia *Corresponding Author, Email: [email protected] ARTICLE INFO ABSTRACT Received: 15 November 2016 The distribution data of Alburnus sava and Telestes souffia has been updated Received in revised form: 1 October 2017 in Croatia in comparison to the previously known data. Alburnus sava is Accepted: 10 October 2017 much more widespread in the Sava drainage and also occurs in the River Available online: 30 October 2017 Sava near the town of Županja, rivers Drina and Bosna. Telestes souffia has a much more restricted range in Croatia than previously believed and is Keywords: only known from the Bregana, small, right tributary of the River Sava on the Alburnus sava Croatian-Slovenian border. Both species are poorly known and threatened. Telestes souffia Distribution data Balkan shemaya Western vairone Riffle dace How to Cite Vucić M., Sučić I., Jelić D. (2017): New distribution data for Alburnus sava Bogutskaya, Zupančič, Jelić, Diripasko & Naseka, 2017 and Telestes souffia (Risso, 1827) in the Western Balkans. Croatian Journal of Fisheries, 75, 137-142. DOI: 10.1515/cjf-2017-0017 INTRODUCTION depths. This behaviour makes it almost impossible to catch during classical electrofishing.
    [Show full text]
  • Ohrožení Živočichové Ruské Federace
    Univerzita Hradec Králové Pedagogická fakulta Katedra slavistiky Ohrožení živočichové Ruské federace Bakalářská práce Autor: Radek Kozel Studijní program: B1501 Biologie Studijní obor: Biologie se zaměřením na vzdělávání Ruský jazyk se zaměřením na vzdělávání Vedoucí práce: Mgr. Miroslav Půža, Ph.D. Hradec Králové 2016 Prohlášení Prohlašuji, že jsem bakalářskou práci vypracoval samostatně a uvedl jsem všechny pou- žité prameny a literaturu. V Hradci Králové dne 18.4.2016 ….….……………………….. Radek Kozel Poděkování Rád bych poděkoval svému vedoucímu bakalářské práce Mgr. Miroslavu Půžovi, Ph.D. za trpělivost, pomoc a odborné rady při zpracovávání práce. Děkuji také Vladimíře Krátké za pomoc při gramatické a stylistické kontrole textu. Poděkování patří i rodině a přátelům za podporu v průběhu celého studia. Anotace KOZEL, Radek. Ohrožení živočichové Ruské federace. Hradec Králové: Pedagogická fakulta, Univerzita Hradec Králové, 2014/2015. Cílem bakalářské práce je vytvořit přehled vybraných druhů ohrožených živočichů Ruské federace. Bakalářská práce se zabývá ohroženými druhy živočichů na území Ruské federace. Ohrožené druhy živočichů v Ruské federaci se liší svým stupněm ohro- žení i důvody, které k jejich zařazení na seznam ohrožených živočichů vedly. Klíčová slova: ohrožené druhy živočichů, Ruská federace, stupeň ohrožení Annotation KOZEL, Radek. Endangered Animals of the Russian Federation. Hradec Králové: Fa- culty of Education, University of Hradec Králové, 2014/2015. Bachelor Degree Thesis. The aim of this work is to create an overview of selected species of the endangered animals of the Russian Federation. The bachelor thesis deals with the endangered spe- cies of animals in the area of the Russian Federation. The endangered species of animals in the Russian Federation differ in their degree of protection as well as reasons, which led for their inclusion on the list of endangered species.
    [Show full text]
  • Chondrostoma Soetta Region: 1 Taxonomic Authority: Bonaparte, 1840 Synonyms: Common Names: Savetta Italian Order: Cypriniformes Family: Cyprinidae Notes on Taxonomy
    Chondrostoma soetta Region: 1 Taxonomic Authority: Bonaparte, 1840 Synonyms: Common Names: Savetta Italian Order: Cypriniformes Family: Cyprinidae Notes on taxonomy: General Information Biome Terrestrial Freshwater Marine Geographic Range of species: Habitat and Ecology Information: Restricted to northern Italy, the southern part of Switzerland. It has A deepwater lacustrine species that also inhabits large rivers. It been introduced in some Italian lakes. It is locally extinct in Slovenia migrates from the lake to its tributaries for spawning in spring. and the Isonzo river basin in Italy due to the introduction of Chondrostoma nasus, a practice still implemented. Introductions in rivers of central Italy was often a misidentification for C. genei. Several present records for C. soetta are probably a misidentification for C. nasus, due to similarity between these two species. As an example of how the alien species are spread now in Italy, in rivers from the Rovigo Province in eastern Italy, were C. soetta is still reported, the biomass of all native species was found to be about 22% of whole ichthyofauna. Conservation Measures: Threats: Listed in Annex II of the Habitats Directive of EU and in the Appendix III Dams, water pollution and extraction, and introduction of alien species of the Bern Convention. as Rutilus rutilus, Silurus glanis and Chondrostoma nasus. The reduction in suitable spawning places due to pollution (agriculture) and to water extraction is of major concern. Other threats to the species are predation by cormorants, where in several places of Italy have become a serious pest and destroyed a large amount of fishes, especially in torrents or small river were the fishes migrate to for reproduction.
    [Show full text]
  • Danube Cycle Path Cycling Holidays
    Z:\Allgemeines Profil\Marketing\Präsentationsmappe\4. Vorlagen und Allgemeines\Neue Vorlagen nach CD ab 2015 8 days | approx. 315 km DANUBE CYCLE PATH Schlögener Schlinge at Danube cycle path © OÖ Touristik GmbH Tours that are as individual as you! CYCLING HOLIDAYS DONAUESCHINGEN – DONAUWÖRTH reach Tuttlingen. The Danube winds bike trail or take the highly recommended Donaueschingen in Brigach route along the rivers Ach and Blau via © Radweg-Reisen through the rocks of the Swabian Alps. Blaubeuren with the impressive "Blautopf" Day 3: Mühlheim/Fridingen – Sigmaringen/ (Blue Pot). Your final destination is Ulm on Scheer (approx. 45 – 60 km) The bike trail the border to Bavaria. continues beside the river, past romantic mills and picturesque corners of the valley. Day 6: Ulm – Lauingen/Dillingen Soon Wildenstein Castle comes into view. (approx. 50 – 55 km) After breakfast you You continue to Sigmaringen. Here you can leave Ulm on the well signposted Danube see one of Europe's largest private weap- Cycle Path and pass the frontier between ons collections. Baden-Wuerttemberg and Bavaria. The bike trail leads you via Weißingen to Leipheim, Day 4: Sigmaringen/Scheer – Region Ober- where the St. Veit Church, the Castle, the Day 1: Individual arrival in Donau- marchtal (approx. 50 – 70 km) Today's eschingen The Brigach and Breg Black town walls and city towers are worth a route starts out in the lovely forests and visit. Later on the route takes you via Forest Rivers join to form the Danube near meadows of the open countryside of the the town, but even the Romans thought the Gundelfingen into the medieval ducal town Danube valley.
    [Show full text]
  • Identification and Modelling of a Representative Vulnerable Fish Species for Pesticide Risk Assessment in Europe
    Identification and Modelling of a Representative Vulnerable Fish Species for Pesticide Risk Assessment in Europe Von der Fakultät für Mathematik, Informatik und Naturwissenschaften der RWTH Aachen University zur Erlangung des akademischen Grades eines Doktors der Naturwissenschaften genehmigte Dissertation vorgelegt von Lara Ibrahim, M.Sc. aus Mazeraat Assaf, Libanon Berichter: Universitätsprofessor Dr. Andreas Schäffer Prof. Dr. Christoph Schäfers Tag der mündlichen Prüfung: 30. Juli 2015 Diese Dissertation ist auf den Internetseiten der Universitätsbibliothek online verfügbar Erklärung Ich versichere, dass ich diese Doktorarbeit selbständig und nur unter Verwendung der angegebenen Hilfsmittel angefertigt habe. Weiterhin versichere ich, die aus benutzten Quellen wörtlich oder inhaltlich entnommenen Stellen als solche kenntlich gemacht zu haben. Lara Ibrahim Aachen, am 18 März 2015 Zusammenfassung Die Zulassung von Pflanzenschutzmitteln in der Europäischen Gemeinschaft verlangt unter anderem eine Abschätzung des Risikos für Organismen in der Umwelt, die nicht Ziel der Anwendung sind. Unvertretbare Auswirkungen auf den Naturhalt sollen vermieden werden. Die ökologische Risikoanalyse stellt die dafür benötigten Informationen durch eine Abschätzung der Exposition der Organismen und der sich daraus ergebenden Effekte bereit. Die Effektabschätzung beruht dabei hauptsächlich auf standardisierten ökotoxikologischen Tests im Labor mit wenigen, oft nicht einheimischen Stellvertreterarten. In diesen Tests werden z. B. Effekte auf das Überleben, das Wachstum und/oder die Reproduktion von Fischen bei verschiedenen Konzentrationen der Testsubstanz gemessen und Endpunkte wie die LC50 (Lethal Concentrations for 50%) oder eine NOEC (No Observed Effect Concentration, z. B. für Wachstum oder Reproduktionsparameter) abgeleitet. Für Fische und Wirbeltiere im Allgemeinen beziehen sich die spezifischen Schutzziele auf das Überleben von Individuen und die Abundanz und Biomasse von Populationen.
    [Show full text]
  • Bringing Nature Back Through LIFE
    Bringing nature back through LIFE The EU LIFE programme’s impact on nature and society Study EnvironmentSocial Europe & Climate Action EUROPEAN COMMISSION ENVIRONMENT DIRECTORATE-GENERAL The contents of the publication “Bringing nature back through LIFE - The EU LIFE programme’s impact on nature and society” do not necessarily reflect the opinions of the institutions of the European Union. Edited by Ben Delbaere Main authors: Lynne Barratt, An Bollen, Ben Delbaere, John Houston, Jan Sliva and Darline Velghe Contributions by: María José Aramburu, Andrej Bača, Oskars Beikulis, Lars Borrass, Anne Calabrese, Stefania Dall’Olio, Jean-Paul Herremans, Sonja Jaari, Bent Jepsen, Mitja Kaligarič, Anastasia Koutsolioutsou, Andras Kovacs, Maud Latruberce, Ioana Gabriela Lucaciu, João Salgado, Camilla Strandberg Panelius, Audrey Thenard, Stanislaw Tworek, Ivaylo Zafirov. Cover photo: Lake Cerknica - LIFE16 NAT/SI/000708 - © Jošt Stergaršek This document has been prepared for EASME by the NEEMO LIFE Team under Framework Contract EASME/LIFE/2018/001 Contract management and editor in EASME, B.3 Unit, LIFE: Sylvia Barova Suggested citation: EASME (2020) Bringing nature back through LIFE. Executive Agency for Small and Medium-sized Enterprises, Brussels. LEGAL NOTICE This document has been prepared for EASME, but it reflects the views of the authors only. The Agency cannot be held responsible for any use for any use of the information contained therein. GETTING IN TOUCH WITH THE EU In person There are hundreds of Europe Direct information centres throughout the European Union. You can find the address of the centre nearest you at: http://europa.eu/contact On the phone or by email Europe Direct is a service to help you answer your questions about the European Union.
    [Show full text]
  • Turnasuyu Ve Curi Derelerinin (Ordu) Balik Faunasinin Belirlenmesi
    T.C. ORDU ÜNİVERSİTESİ FEN BİLİMLERİ ENSTİTÜSÜ TURNASUYU VE CURİ DERELERİNİN (ORDU) BALIK FAUNASININ BELİRLENMESİ RESUL İSKENDER Bu tez, Biyoloji Anabilim Dalında Yüksek Lisans derecesi için hazırlanmıştır. ORDU 2013 TEŞEKKÜR Çalışmalarım süresince ilgi ve desteğini yanımda hissettiğim, bilgi ve tecrübelerinden her zaman yararlandığım değerli danışman hocam Sayın Doç. Dr. Derya BOSTANCI’ya teşekkürlerimi sunarım. Ayrıca örneklerin teşhis edilmesinde, çalışmalarımın ve sonuçlarının değerlendirilmesinde görüş ve önerilerinden yararlandığım değerli ikinci danışman hocam Sayın Yrd. Doç. Dr. Selma HELLİ’ye teşekkürlerimi sunarım. Laboratuvar çalışmalarım ve tezimin hazırlanması boyunca desteklerini esirgemeyen Arş. Gör. Seda KONTAŞ, Gülşah KESKİN ve Muammer DARÇIN’a çok teşekkür ederim. Eğitimimin her aşamasında maddi manevi desteğini esirgemeyen, her zaman yanımda olup bana her konuda destek olan ve beni hiçbir zaman yalnız bırakmayıp, bugünlere gelmemi sağlayan değerli aileme teşekkürü bir borç bilirim. Bu tez Ordu Üniversitesi BAP Birimi tarafından TF-1238 kodlu proje ile desteklenmiştir. i TEZ BİLDİRİMİ Tez yazım kurallarına uygun olarak hazırlanan bu tezin yazılmasında bilimsel ahlak kurallarına uyulduğunu, başkalarının eserlerinden yararlanılması durumunda bilimsel normlara uygun olarak atıfta bulunulduğunu, tezin içerdiği yenilik ve sonuçların başka bir yerden alınmadığını, kullanılan verilerde herhangi bir tahrifat yapılmadığını, tezin herhangi bir kısmının bu üniversite veya başka bir üniversitedeki başka bir tez çalışması olarak sunulmadığını beyan ederim. Resul İSKENDER Not: Bu tezde kullanılan özgün ve başka kaynaktan yapılan bildirişlerin, çizelge, şekil ve fotoğrafların kaynak gösterilmeden kullanımı, 5846 sayılı Fikir ve Sanat Eserleri Kanunundaki hükümlere tabidir. ii ÖZET TURNASUYU VE CURİ DERELERİNİN (ORDU) BALIK FAUNASININ BELİRLENMESİ Resul İSKENDER Ordu Üniversitesi Fen Bilimleri Enstitüsü Biyoloji Anabilim Dalı, 2013 Yüksek Lisans Tezi, 75 s. I.Danışman: Doç.
    [Show full text]
  • Teleostei, Clupeiformes)
    Old Dominion University ODU Digital Commons Biological Sciences Theses & Dissertations Biological Sciences Fall 2019 Global Conservation Status and Threat Patterns of the World’s Most Prominent Forage Fishes (Teleostei, Clupeiformes) Tiffany L. Birge Old Dominion University, [email protected] Follow this and additional works at: https://digitalcommons.odu.edu/biology_etds Part of the Biodiversity Commons, Biology Commons, Ecology and Evolutionary Biology Commons, and the Natural Resources and Conservation Commons Recommended Citation Birge, Tiffany L.. "Global Conservation Status and Threat Patterns of the World’s Most Prominent Forage Fishes (Teleostei, Clupeiformes)" (2019). Master of Science (MS), Thesis, Biological Sciences, Old Dominion University, DOI: 10.25777/8m64-bg07 https://digitalcommons.odu.edu/biology_etds/109 This Thesis is brought to you for free and open access by the Biological Sciences at ODU Digital Commons. It has been accepted for inclusion in Biological Sciences Theses & Dissertations by an authorized administrator of ODU Digital Commons. For more information, please contact [email protected]. GLOBAL CONSERVATION STATUS AND THREAT PATTERNS OF THE WORLD’S MOST PROMINENT FORAGE FISHES (TELEOSTEI, CLUPEIFORMES) by Tiffany L. Birge A.S. May 2014, Tidewater Community College B.S. May 2016, Old Dominion University A Thesis Submitted to the Faculty of Old Dominion University in Partial Fulfillment of the Requirements for the Degree of MASTER OF SCIENCE BIOLOGY OLD DOMINION UNIVERSITY December 2019 Approved by: Kent E. Carpenter (Advisor) Sara Maxwell (Member) Thomas Munroe (Member) ABSTRACT GLOBAL CONSERVATION STATUS AND THREAT PATTERNS OF THE WORLD’S MOST PROMINENT FORAGE FISHES (TELEOSTEI, CLUPEIFORMES) Tiffany L. Birge Old Dominion University, 2019 Advisor: Dr. Kent E.
    [Show full text]
  • Ecological Traits of Squalius Lucumonis (Actinopterygii, Cyprinidae) and Main Differences with Those of Squalius Squalus in the Tiber River Basin (Italy)
    Knowledge and Management of Aquatic Ecosystems (2013) 409, 04 http://www.kmae-journal.org c ONEMA, 2013 DOI: 10.1051/kmae/2013049 Ecological traits of Squalius lucumonis (Actinopterygii, Cyprinidae) and main differences with those of Squalius squalus in the Tiber River Basin (Italy) D. Giannetto(1),,A.Carosi(2), L. Ghetti(3), G. Pedicillo(1),L.Pompei(1), M. Lorenzoni(1) Received January 29, 2013 Revised April 11, 2013 Accepted April 11, 2013 ABSTRACT Key-words: Squalius lucumonis (Bianco, 1983) is an endemic species restricted to endemic three river basins in central Italy and listed as endangered according to species, IUCN Red List. The aim of this research was to increase the information Squalius on ecological preferences of this species and to focus on its differences lucumonis, with S. squalus (Bonaparte, 1837). Data collected in 86 different water- Squalius courses throughout Tiber River basin were analysed in the research. For squalus, each of the 368 river sectors examined, the main environmental parame- longitudinal ters and the fish community were considered. The information were anal- gradient, ysed by means of the Canonical Correspondence Analysis (CCA) while the fish assemblage differences in ecological traits between S. lucumonis and S. squalus were compared by ANOVA. The results of the study showed significant differ- ences in the ecological preferences of the two species: the S. lucumonis showed predilection for smaller watercourses characterised by a lower number of species and a higher degree of integrity of fish community than S. squalus This information allowed to increase the basic knowledge on population biology and ecology of S.
    [Show full text]