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The Effect of Water Temperature on Aquatic Organisms: a Review of Knowledge and Methods for Assessing Biotic Responses to Temperature
The effect of water temperature on aquatic organisms: a review of knowledge and methods for assessing biotic responses to temperature Report to the Water Research Commission by Helen Dallas The Freshwater Consulting Group Freshwater Research Unit Department of Zoology University of Cape Town WRC Report No. KV 213/09 30 28 26 24 22 C) o 20 18 16 14 Temperature ( 12 10 8 6 4 Jul '92 Jul Oct '91 Apr '92 Jun '92 Jan '93 Mar '92 Feb '92 Feb '93 Aug '91 Nov '91 Nov '91 Dec Aug '92 Sep '92 '92 Nov '92 Dec May '92 Sept '91 Month and Year i Obtainable from Water Research Commission Private Bag X03 GEZINA, 0031 [email protected] The publication of this report emanates from a project entitled: The effect of water temperature on aquatic organisms: A review of knowledge and methods for assessing biotic responses to temperature (WRC project no K8/690). DISCLAIMER This report has been reviewed by the Water Research Commission (WRC) and approved for publication. Approval does not signify that the contents necessarily reflect the views and policies of the WRC, nor does mention of trade names or commercial products constitute endorsement or recommendation for use ISBN978-1-77005-731-9 Printed in the Republic of South Africa ii Preface This report comprises five deliverables for the one-year consultancy project to the Water Research Commission, entitled “The effect of water temperature on aquatic organisms – a review of knowledge and methods for assessing biotic responses to temperature” (K8-690). Deliverable 1 (Chapter 1) is a literature review aimed at consolidating available information pertaining to water temperature in aquatic ecosystems. -
The Global Status of Freshwater Fish Age Validation Studies and a Prioritization Framework for Further Research Jonathan J
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Nebraska Cooperative Fish & Wildlife Research Nebraska Cooperative Fish & Wildlife Research Unit -- Staff ubP lications Unit 2015 The Global Status of Freshwater Fish Age Validation Studies and a Prioritization Framework for Further Research Jonathan J. Spurgeon University of Nebraska–Lincoln, [email protected] Martin J. Hamel University of Nebraska-Lincoln, [email protected] Kevin L. Pope U.S. Geological Survey—Nebraska Cooperative Fish and Wildlife Research Unit,, [email protected] Mark A. Pegg University of Nebraska-Lincoln, [email protected] Follow this and additional works at: http://digitalcommons.unl.edu/ncfwrustaff Part of the Aquaculture and Fisheries Commons, Environmental Indicators and Impact Assessment Commons, Environmental Monitoring Commons, Natural Resource Economics Commons, Natural Resources and Conservation Commons, and the Water Resource Management Commons Spurgeon, Jonathan J.; Hamel, Martin J.; Pope, Kevin L.; and Pegg, Mark A., "The Global Status of Freshwater Fish Age Validation Studies and a Prioritization Framework for Further Research" (2015). Nebraska Cooperative Fish & Wildlife Research Unit -- Staff Publications. 203. http://digitalcommons.unl.edu/ncfwrustaff/203 This Article is brought to you for free and open access by the Nebraska Cooperative Fish & Wildlife Research Unit at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Nebraska Cooperative Fish & Wildlife Research Unit -- Staff ubP lications by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. Reviews in Fisheries Science & Aquaculture, 23:329–345, 2015 CopyrightO c Taylor & Francis Group, LLC ISSN: 2330-8249 print / 2330-8257 online DOI: 10.1080/23308249.2015.1068737 The Global Status of Freshwater Fish Age Validation Studies and a Prioritization Framework for Further Research JONATHAN J. -
Jlb Smith Institute of Ichthyology
ISSN 0075-2088 J.L.B. SMITH INSTITUTE OF ICHTHYOLOGY GRAHAMSTOWN, SOUTH AFRICA SPECIAL PUBLICATION No. 56 SCIENTIFIC AND COMMON NAMES OF SOUTHERN AFRICAN FRESHWATER FISHES by Paul H. Skelton November 1993 SERIAL PUBLICATIONS o f THE J.L.B. SMITH INSTITUTE OF ICHTHYOLOGY The Institute publishes original research on the systematics, zoogeography, ecology, biology and conservation of fishes. Manuscripts on ancillary subjects (aquaculture, fishery biology, historical ichthyology and archaeology pertaining to fishes) will be considered subject to the availability of publication funds. Two series are produced at irregular intervals: the Special Publication series and the Ichthyological Bulletin series. Acceptance of manuscripts for publication is subject to the approval of reviewers from outside the Institute. Priority is given to papers by staff of the Institute, but manuscripts from outside the Institute will be considered if they are pertinent to the work of the Institute. Colour illustrations can be printed at the expense of the author. Publications of the Institute are available by subscription or in exchange for publi cations of other institutions. Lists of the Institute’s publications are available from the Publications Secretary at the address below. INSTRUCTIONS TO AUTHORS Manuscripts shorter than 30 pages will generally be published in the Special Publications series; longer papers will be considered for the Ichthyological Bulletin series. Please follow the layout and format of a recent Bulletin or Special Publication. Manuscripts must be submitted in duplicate to the Editor, J.L.B. Smith Institute of Ichthyology, Private Bag 1015, Grahamstown 6140, South Africa. The typescript must be double-spaced throughout with 25 mm margins all round. -
Environmental Impact Assessment for the Blyvoor Gold Mining Project, West Rand, Gauteng
Environmental Impact Assessment for the Blyvoor Gold Mining Project, West Rand, Gauteng Biodiversity Report Project Number: BVG4880 Prepared for: Blyvoor Gold Capital (Pty) Ltd October 2018 _______________________________________________________________________________________ Digby Wells and Associates (South Africa) (Pty) Ltd Co. Reg. No. 2010/008577/07. Turnberry Office Park, 48 Grosvenor Road, Bryanston, 2191. Private Bag X10046, Randburg, 2125, South Africa Tel: +27 11 789 9495, Fax: +27 11 069 6801, [email protected], www.digbywells.com _______________________________________________________________________________________ Directors: GE Trusler (C.E.O), GB Beringer, LF Koeslag, J Leaver (Chairman)*, NA Mehlomakulu*, DJ Otto, RA Williams* *Non-Executive _______________________________________________________________________________________ This document has been prepared by Digby Wells Environmental. Report Type: Biodiversity Report Environmental Impact Assessment for the Blyvoor Gold Project Name: Mining Project, West Rand, Gauteng Project Code: BVG4880 Name Responsibility Signature Date Aquatics and Kieren Bremner wetlands surveying October 2018 and report writing Kathryn Roy Report writing October 2018 Fauna and flora Rudi Greffrath October 2018 baseline Brett Coutts OpsCo review October 2018 This report is provided solely for the purposes set out in it and may not, in whole or in part, be used for any other purpose without Digby Wells Environmental prior written consent. Digby Wells Environmental i Biodiversity Report Environmental Impact Assessment for the Blyvoor Gold Mining Project, West Rand, Gauteng BVG4880 EXECUTIVE SUMMARY Digby Wells Environmental (hereinafter Digby Wells) was appointed by Blyvoor Gold Capital (Pty) Ltd (hereafter Blyvoor Gold) to undertake a freshwater impact assessment and fauna and flora baseline update as part of an Environmental Application Process to obtain the required authorisation for the Blyvoor Gold mining operation. -
Conference Proceedings 2006
FOSAF THE FEDERATION OF SOUTHERN AFRICAN FLYFISHERS PROCEEDINGS OF THE 10 TH YELLOWFISH WORKING GROUP CONFERENCE STERKFONTEIN DAM, HARRISMITH 07 – 09 APRIL 2006 Edited by Peter Arderne PRINTING & DISTRIBUTION SPONSORED BY: sappi 1 CONTENTS Page List of participants 3 Press release 4 Chairman’s address -Bill Mincher 5 The effects of pollution on fish and people – Dr Steve Mitchell 7 DWAF Quality Status Report – Upper Vaal Management Area 2000 – 2005 - Riana 9 Munnik Water: The full picture of quality management & technology demand – Dries Louw 17 Fish kills in the Vaal: What went wrong? – Francois van Wyk 18 Water Pollution: The viewpoint of Eco-Care Trust – Mornē Viljoen 19 Why the fish kills in the Vaal? –Synthesis of the five preceding presentations 22 – Dr Steve Mitchell The Elands River Yellowfish Conservation Area – George McAllister 23 Status of the yellowfish populations in Limpopo Province – Paul Fouche 25 North West provincial report on the status of the yellowfish species – Daan Buijs & 34 Hermien Roux Status of yellowfish in KZN Province – Rob Karssing 40 Status of the yellowfish populations in the Western Cape – Dean Impson 44 Regional Report: Northern Cape (post meeting)– Ramogale Sekwele 50 Yellowfish conservation in the Free State Province – Pierre de Villiers 63 A bottom-up approach to freshwater conservation in the Orange Vaal River basin – 66 Pierre de Villiers Status of the yellowfish populations in Gauteng Province – Piet Muller 69 Yellowfish research: A reality to face – Dr Wynand Vlok 72 Assessing the distribution & flow requirements of endemic cyprinids in the Olifants- 86 Doring river system - Bruce Paxton Yellowfish genetics projects update – Dr Wynand Vlok on behalf of Prof. -
ABSTRACT As Early As 1987, the US Environmental Protection
Registration Number: 2006/217972/23 NPO NUMBER: 062986-NPO ABSTRACT As early as 1987, the US Environmental Protection Agency recognised that “.....problems related to mining waste may be rated as second only to global warming and stratospheric ozone depletion in terms of ecological risk. The release to the environment of mining waste can result in profound, generally irreversible destruction of ecosystems1.” Gold tailings dams from the Witwatersrand Basin usually contain elevated amounts of heavy metals and radionuclides. With slimes dams in the goldfields of the Witwatersrand Basin 2 covering an area of about 400 km and containing some 430 000 tons of U3O8, and 6 billion tons of iron pyrite tailings, they constitute an environmental problem of extraordinary spatial dimensions. Due to inadequate design, poor management and neglect, these tailings dams have 1 CSIR. Briefing Note August 2009. Acid Mine Drainage in South Africa. Dr. Pat Manders. Director, Natural Resources and the Environment. European Environmental Bureau (EEB). 2000. The environmental performance of the mining industry and the action necessary to strengthen European legislation in the wake of the Tisza-Danube pollution. EEB Document no 2000/016. 32 p 1 been subject to varying degrees of water and wind erosion. Effects range from water pollution, the result of acid mine drainage, and air pollution in the form of airborne dust from unrehabilitated or partially rehabilitated and reprocessed tailings dams. As a result of acid mine drainage (AMD), from point discharges and seepage uranium is released into the groundwater and fluvial systems. (Figure 1) Figure 1 2 West Wits Pit Figure 2 Recent public domain official and scientific studies indicate that there is active leaching of uranium from the tailings, transport of soluble uranium species through water systems, with subsequent deposition of insoluble uranium species in sediments of fluvial systems. -
YWG Conference Proceedings 2014
FOSAF PROCEEDINGS OF THE 18 TH YELLOWFISH WORKING GROUP CONFERENCE BLACK MOUNTAIN HOTEL, THABA ´NCHU, FREE STATE PROVINCE Image courtesy of Carl Nicholson EDITED BY PETER ARDERNE 1 18 th Yellowfish Working Group Conference CONTENTS Page Participants 3 Opening address – Peter Mills 4 State of the rivers of the Kruger National Park – Robin Petersen 6 A fish kill protocol for South Africa – Byron Grant 10 Phylogeographic structure in the KwaZulu-Natal yellowfish – Connor Stobie 11 Restoration of native fishes in the lower Rondegat River after alien fish eradication: 15 an overview of a successful conservation intervention.- Darragh Woodford Yellowfish behavioural work in South Africa: past, present and future research – 19 Gordon O’Brien The occurrence and distribution of yellowfish in state dams in the Free State. – Leon 23 Barkhuizen; J.G van As 2 & O.L.F Weyl 3 Yellowfish and Chiselmouths: Biodiversity Research and its conservation 24 implications - Emmanuel Vreven Should people be eating fish from the Olifants River, Limpopo Province? 25 – Sean Marr A review of the research findings on the Xikundu Fishway & the implications for 36 fishways in the future – Paul Fouche´ Report on the Vanderkloof Dam- Francois Fouche´ 48 Karoo Seekoei River Nature Reserve – P C Ferreira 50 Departmental report: Biomonitoring in the lower Orange River within the borders 54 of the Northern Cape Province – Peter Ramollo Free State Report – Leon Barkhuizen 65 Limpopo Report – Paul Fouche´ 68 Conference summary – Peter Mills 70 Discussion & Comment following -
Chapter Two: Study Areas with General Materials and Methods
Chapter Two: Study Areas with General Materials and Methods 40 2 Study areas with general materials and methods 2.1 Introduction to study areas To reach the aims and objectives for this study, one lentic and one lotic system within the Vaal catchment had to be selected. The lentic component of the study involved a manmade lake or reservoir, suitable for this radio telemetry study. Boskop Dam, with GPS coordinates 26o33’31.17” (S), 27 o07’09.29” (E), was selected as the most representative (various habitats, size, location, fish species, accessibility) site for this radio telemetry study. For the lotic component of the study a representative reach of the Vaal River flowing adjacent to Wag ‘n Bietjie Eco Farm, with GPS coordinates 26°09’06.69” (S), 27°25’41.54” (E), was selected (Figure 3). Figure 3: Map of the two study areas within the Vaal River catchment, South Africa Boskop Dam Boskop manmade lake also known as Boskop Dam is situated 15 km north of Potchefstroom (Figure 4) in the Dr. Kenneth Kaunda District Municipality in the North West Province (Van Aardt and Erdmann, 2004). The dam is part of the Mooi River water scheme and is currently the largest reservoir built on the Mooi River (Koch, 41 1975). Apart from Boskop Dam, two other manmade lakes can be found on the Mooi River including Kerkskraal and Lakeside Dam (also known as Potchefstroom Dam). The Mooi River rises in the north near Koster and then flows south into Kerkskraal Dam which feeds Boskop Dam. Boskop Dam stabilises the flow of the Mooi River and two concrete canals convey water from the Boskop Dam to a large irrigation area. -
Spatio-Temporal Variation in Length-Frequency and Salinity Tolerance of Dominant Fishes Utilizing the Orange River-Estuary Continuum
WIJAS 2: 19–32 (2020) Spatio-temporal variation in length-frequency and salinity tolerance of dominant fishes utilizing the Orange River-Estuary Continuum FP Nashima Department of Fisheries and Aquatic Sciences, University of Namibia, P.O Box 462, Henties Bay, Namibia Abstract The length-frequency distribution of the dominant species of euryhaline marine Chelon richardsonii, estuarine Gilchristella aestuaria and freshwater species Labeobarbus aeneus, Mesobola brevianalis and Pseudocrenilabrus philander were investigated seasonally along the Orange River Estuary Continuum (OREC) during high-flow and low-flow periods, conducted in eight years, within 15 years (2004-2018). We sampled fish using a seine net at 18 sites spanning from the mouth of the estuary up to 35 km upstream. The length-frequency distributions of all species did not differ between the high-flow and low-flow season. Spatial differentiation in size-frequency distribution of all freshwater taxon was recorded along the river- estuarine continuum but not for C. richardsonii and G. aestuaria. Total catch-per-unit-effort (CPUE) was low for both M. brevianalis and P. philander, and their abundance declined downstream into the estuarine region as expected for these two freshwater species. A positive correlation between salinity and fish length of all five species was found, demonstrating that juvenile fishes, in particular, freshwater species are less salt-tolerant than the adults. It is concluded that the lower OREC provides a vital fish nursery habitat suitable for growth and development, particularly for marine C. richardsonii and estuarine G. aestuaria. Keywords: Catch-per-unit-effort, distribution, euryhaline, salinity, stenohaline.1 1. Introduction Length-frequency distribution measurements are fundamental to many aspects of fisheries science as they aid in understanding the state of the fish population (Pope et al., 2010). -
THESIS Submitted in Fulfilment of the Requirements for the Degree of MASTER of SCIENCE of Rhodes University
THE KARYOLOGY AND TAXONOMY OF THE SOUTHERN AFRICAN YELLOWFISH (PISCES: CYPRINIDAE) THESIS Submitted in Fulfilment of the Requirements for the Degree of MASTER OF SCIENCE of Rhodes University by LAWRENCE KEITH OELLERMANN December, 1988 ABSTRACT The southern African yellowfish (Barbus aeneus, ~ capensls, .!L. kimberleyensis, .!L. natalensis and ~ polylepis) are very similar, which limits the utility of traditional taxonomic methods. For this reason yellowfish similarities were explored using multivariate analysis and karyology. Meristic, morphometric and Truss (body shape) data were examined using multiple discriminant, principal component and cluster analyses. The morphological study disclosed that although the species were very similar two distinct groups occurred; .!L. aeneus-~ kimberleyensis and ~ capensis-~ polylepis-~ natalensis. Karyology showed that the yellowfish were hexaploid, ~ aeneus and IL... kimberleyensis having 148 chromosomes while the other three species had 150 chromosomes. Because the karyotypes of the species were variable the fundamental number for each species was taken as the median value for ten spreads. Median fundamental numbers were ~ aeneus ; 196, .!L. natalensis ; 200, ~ kimberleyensis ; 204, ~ polylepis ; 206 and ~ capensis ; 208. The lower chromosome number and higher fundamental number was considered the more apomorphic state for these species. Silver-staining of nucleoli showed that the yellowfish are probably undergoing the process of diploidization. Southern African Barbus and closely related species used for outgroup comparisons showed three levels of ploidy. The diploid species karyotyped were ~ anoplus (2N;48), IL... argenteus (2N;52), ~ trimaculatus (2N;42- 48), Labeo capensis (2N;48) and k umbratus (2N;48); the tetraploid species were B . serra (2N;102), ~ trevelyani (2N;±96), Pseudobarbus ~ (2N;96) and ~ burgi (2N;96); and the hexaploid species were ~ marequensis (2N;130-150) and Varicorhinus nelspruitensis (2N;130-148). -
Hexaploidy in Yellowfish Species (Barbus, Pisces, Cyprinidae) from Southern Africa
Journal of Fish Biology (1990) 37, 105-1 15 Hexaploidy in yellowfish species (Barbus, Pisces, Cyprinidae) from southern Africa L. K. OELLERMANNAND P. H. SICELTON* J.L.B. Smith Institute of Ichthyology, Private Bag 1015, Grahamstown 6140, Republic of South Africa (Received 18 July 1989, Accepted I February 1990) Five small-scaled yellowfish (large Burbus spp.) from southern Africa are shown to have modal 148 or 150chromosomes. Themajority ofcyprinid species have 2N = 50chromosomes, indicating that the yellowfish karyotype is hexaploid in origin. However, as there is no indication that the species are unisexual or that normal reproduction occurs by any means other than bisexual fertilization, the yellowfish karyotype is considered to have reverted to a diploid condition. Key words: karyology; yellowfish; Burbus; hexaploidy; southern Africa. I. INTRODUCTION The name ' yellowfish ' is given to several large-sized Burbus species in southern Africa (Jubb, 1967). The yellowfish fall into two groups on the basis of scale size. The group with smaller scales consists of five recognized species distributed in the Orange River system and adjacent drainage systems (Skelton, 1986). The second group, with larger scales, consists of two species, Barbus rnarequensis Smith, 1841 and Barbus codringtonii Boulenger, 1908, distributed in east coastal drainages from the Phongola River to the Zambezi River system. This study concerns the five small-scaled yellowfish species, viz. Barbus cupensis Smith, 1841 from the Olifants River system, Burbus aeneus (Burchell, 1822) and Burbus kimberleyensis Gilchrist & Thompson, 1913 from the Orange River system, Barbus polylepis Boulenger, 1907 from the Limpopo, lncomati and Phongola River systems, and Burbus natalensis Castelnau, 1861 from the rivers of Natal. -
Ecological Parameters of Selected Helminth
ECOLOGICAL PARAMETERS OF SELECTED HELMINTH SPECIES IN LABEOBARBUS AENEUS AND LABEOBARBUS KIMBERLEYENSIS IN THE VAAL DAM, AND AN EVALUATION OF THEIR INFLUENCE ON INDICATORS OF ENVIRONMENTAL HEALTH By ALESSANDRA BERTASSO SHORT DISSERTATION submitted in partial fulfilment of the requirements for the degree MASTER OF SCIENCE in ENVIRONMENTAL MANAGEMENT in the FACULTY OF SCIENCE at the RAND AFRIKAANS UNIVERSITY SUPERVISOR: PROF. A. AVENANT-OLDEWAGE MAY 2004 ACKNOWLEDGEMENTS My sincere thanks and gratitude go to: ∗ My partner in life and love, Dwayne, for all his support, love and continual motivation. ∗ My supervisor, Professor A. Avenant-Oldewage, for her support and patience throughout my study. ∗ Rand Water for making water quality data available. ∗ Rand Afrikaans University for financial support. ∗ Zoology Department at RAU for use of facilities. ∗ The staff and students at the Zoology Department for assistance in field work. ∗ Groot Eiland staff for their help and use of facilities. ∗ S.N. Mashego for his assistance in identifying the tapeworms collected. ∗ Riette Eiselen from RAU Statkon for statistical analyses of my data. ∗ My colleague and friend, Bronwyn Gernet for assisting with the maps. ∗ My Parents, for giving me the opportunity to further my studies and for their unconditional love and support. ABSTRACT Surveys conducted by the Rand Afrikaans University fish parasitology group have shown unexpectedly high numbers of helminth parasites (endoparasites) in yellowfish species in the Vaal Dam. The high number of helminth parasites can be attributed to a cestode species (Bothriocephalus spp.) which has been introduced with cyprinid fish into South Africa from Asia. It was expected that this opportunistic introduced species, in its high numbers, may affect the accuracy of the fish health assessment index (HAI).