DOCSLIB.ORG

Proposed Aquatic Ecosystem Protection Guideline Values for Pesticides Commonly Used in the Great Barrier Reef Catchment Area

Total Page：16

File Type：pdf, Size：1020Kb

Download full-text PDF Read full-text
Proposed Aquatic Ecosystem Protection Guideline Values for Pesticides Commonly Used in the Great Barrier Reef Catchment Area Proposed aquatic ecosystem protection guideline values for pesticides commonly used in the Great Barrier Reef catchment area: Part 1 (amended) – 2,4-D, Ametryn, Diuron, Glyphosate, Hexazinone, Imazapic, Imidacloprid, Isoxaflutole, Metolachlor, Metribuzin, Metsulfuron-methyl, Simazine and Tebuthiuron. Water Quality and Investigations | Department of Environment and Science 2017 (amended March 2018) Prepared by O. C. King, R. A. Smith, R. M. Mann and M. St. J. Warne. Water Quality and Investigations, Environmental Monitoring and Assessment Science, Science Division, Department of Environment and Science PO Box 5078 Brisbane QLD 4001 © The State of Queensland (Department of Environment and Science) 2017 The Queensland Government supports and encourages the dissemination and exchange of its information. The copyright in this publication is licensed under a Creative Commons Attribution 3.0 Australia (CC BY) licence Under this licence you are free, without having to seek permission from DES, to use this publication in accordance with the licence terms. You must keep intact the copyright notice and attribute the State of Queensland, Department of Environment and Science as the source of the publication. For more information on this licence visit http://creativecommons.org/licenses/by/3.0/au/deed.en Disclaimer This document has been prepared with all due diligence and care, based on the best available information at the time of publication. The department holds no responsibility for any errors or omissions within this document. Any decisions made by other parties based on this document are solely the responsibility of those parties. Information contained in this document is from a number of sources and, as such, does not necessarily represent government or departmental policy. If you need to access this document in a language other than English, please call the Translating and Interpreting Service (TIS National) on 131 450 and ask them to telephone Library Services on +61 7 3170 5725 Citation O. C. King, R. A. Smith, R. M. Mann and M. St. J. Warne. 2017. Proposed aquatic ecosystem protection guideline values for pesticides commonly used in the Great Barrier Reef catchment area: Part 1 (amended) - 2,4-D, Ametryn, Diuron, Glyphosate, Hexazinone, Imazapic, Imidacloprid, Isoxaflutole, Metolachlor, Metribuzin, Metsulfuron-methyl, Simazine, Tebuthiuron. Department of Environment and Science. Brisbane, Queensland, Australia. 296 pp. August 2017 (amended March 2018) Acknowledgements The authors gratefully acknowledge the funding provided by the Commonwealth Government Department of Environment (DoE), Commonwealth Scientific and Industrial Research Organisation (CSIRO), National Environmental Research Programme (NERP), Queensland Department of Environment and Heritage Protection (DEHP) and the Queensland Government Department of Environment and Science (DES). The authors thank Andrew Novic, Gabrielle Dern and Julius Frangos for assistance in quality checking the literature. The authors would also like to acknowledge valuable comments provided by the reviewers (Alicia Hogan, Graeme Batley, John Chapman, Lisa Golding, Merrin Adams, Rick van Dam and several anonymous reviewers) and discussions held with numerous colleagues during the derivation of the revised proposed aquatic ecosystem protection guideline values. Proposed Ecosystem Protection Guideline Values Executive summary The Australian and New Zealand Guideline for Fresh and Marine Water Quality, also referred to as the National Water Quality Guidelines (ANZECC and ARMCANZ 2000), provides toxicity-based default guideline values (formerly referred to as trigger values) for numerous inorganic and organic chemicals of environmental concern, including guideline values for fifty individual pesticides. This number falls well short of the total number of pesticides used in Australia and under-represents many of the pesticides currently used in Great Barrier Reef catchments. The National Water Quality Guidelines are currently being revised as part of the National Water Quality Management Strategy (NWQMS). Under several different funding arrangements, the Science Division of the Queensland Government Department of Environment and Science (DES) (Previously known as Department of Science, Information Technology and Innovation (DSITI)) has been engaged in the derivation of new or revised aquatic ecosystem protection guideline values for 27 pesticides commonly detected in the Great Barrier Reef catchments. All aquatic ecosystem protection guideline values have been derived using the revised method for deriving water quality guidelines for toxicants (Warne et al. 2015). In Australia, water quality guideline values are preferably derived using a species sensitivity distribution (SSD) approach. The intent is that all these aquatic ecosystem protection guideline values are ultimately endorsed as National default guideline values. Until such time that they have received endorsement by the Standing Committee for the Revision of the National Guidelines, these derived guideline values will be termed as proposed aquatic ecosystem protection guideline values. In the interest of brevity, in this report they are also referred to as Proposed Guideline Values (PGV). This report is the first part of a two-part series that presents the Proposed Guideline Values for 27 pesticides commonly detected in both, freshwater catchments and marine waters of the Great Barrier Reef. The Proposed Guideline Values have been split across the two separate reports depending on the funding arrangements under which they were derived. The Proposed Guideline Values for glyphosate, metolachlor, metsulfuron-methyl, and simazine were derived under contract with the Commonwealth Government Department of the Environment (DoE) and the Commonwealth Scientific and Industrial Research Organisation (CSIRO), and were derived for inclusion in the revised Australian and New Zealand Guidelines for Fresh and Marine Water Quality. At the time of writing, publication of the revised Australian and New Zealand Guidelines for Fresh and Marine Water Quality was still pending. The Proposed Guideline Values for 2,4-D, imazapic, isoxaflutole and metribuzin were derived as part of a project funded by the National Environmental Research Programme (NERP). The Proposed Guideline Values for ametryn, diuron, hexazinone, imidacloprid and tebuthiuron were derived as part of a research project funded by the Queensland Department of Science, Information Technology and Innovation (DSITI). This report represents an amendment to the original report published in August 2017. The Proposed Guideline Values for imidacloprid have changed following the discovery of errors in the original derivation. The 13 pesticides presented in Part 1 (this report) were selected based on the priorities of Commonwealth and State government departments and stakeholders. Several of these guidelines are currently being reviewed for endorsement as National guideline values. The 14 pesticides included in Part 2 (King et al. 2017) are also detected regularly in catchments discharging to the GBR lagoon (Wallace et al. 2016). Currently, there are either, no, or only low reliability National i guideline values in existence for these pesticides. As part of a project funded by the Queensland Department of Environment and Heritage Protection (now part of the the Department of Environment and Science), the Queensland Department of Environment and Science has derived Proposed Guideline Values for fresh and marine ecosystems for these 14 pesticides. ii Proposed Ecosystem Protection Guideline Values Background Pesticides in the Great Barrier Reef Pesticides pose a risk to freshwater ecosystems as well as inshore and coastal ecosystems of the Great Barrier Reef (GBR) (Waterhouse et al. 2017). Pesticides in the aquatic environment can cause direct and indirect effects that reduce the resilience of aquatic ecosystems to other stressors. Diffuse sources of pollution from agriculture are the largest contributors of pesticides to the GBR, and include cattle grazing and sugarcane cultivation as the dominant modified land uses (Brodie et al. 2013). In an effort to protect the health and resilience of the GBR from poor water quality, the Reef Water Quality Protection Plan (Reef Plan) was established in 2003 in a joint collaboration by the Australian and Queensland governments (DPC 2013). In 2009, following the release of the Scientific Consensus Statement (Brodie et al. 2008), a comprehensive update of Reef Plan was undertaken. This addressed the elevated levels of pollutants leaving catchments adjacent to the GBR and entering the Reef, with a clear goal1 and specific targets for reducing sediment, nutrient and pesticide loads (DPC 2013). The Reef Plan has since been updated in 2013 with the next version released in 2017. The targets for pesticide reduction originally focused on the loads of five photosystem II herbicides. Since that time, water quality monitoring by the Great Barrier Reef Catchment Loads Monitoring Program and the Marine Monitoring Program (as part of the Paddock to Reef Integrated Monitoring, Modelling and Reporting Program), has demonstrated that there are many different pesticides present in the catchments and the GBR lagoon (Wallace et al. 2016). Indeed, 56 pesticide residues (including seven herbicide metabolites) have been detected in the adjacent catchments, estuaries and wetlands and the GBR lagoon since 2009 (Devlin et al. 2015; Wallace et al. 2016). In 2017, the Reef Plan pesticide targets
Load more

Recommended publications
  • Improving the Utilization of Data for Environmental Risk Assessment
    STATISTICALECO(-TOXICO)LOGY IMPROVINGTHEUTILISATIONOFDATAFOR ENVIRONMENTALRISKASSESSMENT by eduard szöcs from zarneˇ ¸sti / romania Accepted Dissertation thesis for the partial fulfillment of the requirements for a Doctor of Natural Sciences Fachbereich 7: Natur- und Umweltwissenschaften Universität Koblenz-Landau Thesis examiners: Prof. Dr. Ralf B. Schäfer, University Koblenz-Landau Prof. Dr. Ralf Schulz, University Koblenz-Landau Assoc. Prof. Dr. Christian Ritz, University of Copenhagen Date of the oral examination: 25th January 2017 Galileo Few may hear Galileo’s song (calling) A tribulation Adversities Fuel for a living, feeds us all Spirit is fire Uncompromising Hidden hand, protect us from The dead and dying Echo his madness His heresy feeds us all Spirit is fire Uncompromising Hidden hand, protect us from The dead and dying Few may Spirit is fire Feed on the senseless ending Spirit is fire Feed on the senseless ending - Song by Maynard James Keenan ACKNOWLEDGMENTS I thank all the persons that supported me during my studies and this dissertation. My special thanks to my supervisor Prof. Dr. Ralf B. Schäfer for his support throughout the last six years. I am thankful for his openness to my ideas and the opportunities given to follow them, for organising funding throughout this dissertation, for pushing me to sound scientific writing and critical reading, for challenging discussions, not only on statistical eco(-toxico)logy but also outside of the subject area. Many thanks to Prof. Dr. Ralf Schulz for examining this thesis and his influence on me during my undergrad studies. Moreover, I thank Prof. Dr. Engelbert Niehaus for chairing the dissertation committee. Without the continuous support of my parents, Anca and Helmut, this thesis would not have been possible - Thank you! I am grateful to my colleagues, students and other people for asking me tough statistical questions.
    [Show full text]
  • Freshwater Gammarus Species from Europe, North Africa and Adjacent Regions of Asia (Crustacea-Amphipoda)
    FRESHWATER GAMMARUS SPECIES FROM EUROPE, NORTH AFRICA AND ADJACENT REGIONS OF ASIA (CRUSTACEA-AMPHIPODA) PART II. GAMMARUS ROESELI-GROUP AND RELATED SPECIES by GORDAN S. KARAMAN Biological Institute, Titograd, Yugoslavia & SJOUK PINKSTER Institute of Taxonomic Zoology, University of Amsterdam, The Netherlands FRESHWATER GAMMARUS SPECIES FROM EUROPE, NORTH AFRICA AND ADJACENT REGIONS OF ASIA (CRUSTACEA-AMPHIPODA) PART II. GAMMARUS ROESELI-GROUP AND RELATED SPECIES by GORDAN S. KARAMAN Biological Institute, Tito grad, Yugoslavia 8Z SJOUK PINKSTER Institute of Taxonomic Zoology, University of Amsterdam, The Netherlands ABSTRACT 9) For all species complete lists of all studied localities 1) This part of the revision of the freshwater Gammarus are given (except for G. roeseli, for economical reasons), species deals with the G. roeseli-group. Members of this together with two maps in which the distribution is illus- artificial group are characterized by the presence of dorsal trated. processes (carinae) on the metasome segments. RESUME 2) A historical review is given from the first description of G. roeseli and the taxonomic confusion that followed, to 1) Cette deuxieme partie de la revision traite des Gam- the start of this study when 3 species and at least 15 sub- marus d'eau douce du groupe roeseli. Les membres de ce species were known. groupe artificiel sont caracterises par la presence de carenes 3) Where possible, the type material of all these taxa is dorsales sur les segments du metasome. re-examined and compared with hundreds of newly collected 2) Un apercu historique est donne des la premiere samples and material from all major museums in Europe.
    [Show full text]
  • Crustacea-Arthropoda) Fauna of Sinop and Samsun and Their Ecology
    J. Black Sea/Mediterranean Environment Vol. 15: 47- 60 (2009) Freshwater and brackish water Malacostraca (Crustacea-Arthropoda) fauna of Sinop and Samsun and their ecology Sinop ve Samsun illeri tatlısu ve acısu Malacostraca (Crustacea-Arthropoda) faunası ve ekolojileri Mehmet Akbulut1*, M. Ruşen Ustaoğlu2, Ekrem Şanver Çelik1 1 Çanakkale Onsekiz Mart University, Fisheries Faculty, Çanakkale-Turkey 2 Ege University, Fisheries Faculty, Izmir-Turkey Abstract Malacostraca fauna collected from freshwater and brackishwater in Sinop and Samsun were studied from 181 stations between February 1999 and September 2000. 19 species and 4 subspecies belonging to 15 genuses were found in 134 stations. In total, 23 taxon were found: 11 Amphipoda, 6 Decapoda, 4 Isopoda, and 2 Mysidacea. Limnomysis benedeni is the first time in Turkish Mysidacea fauna. In this work at the first time recorded group are Gammarus pulex pulex, Gammarus aequicauda, Gammarus uludagi, Gammarus komareki, Gammarus longipedis, Gammarus balcanicus, Echinogammarus ischnus, Orchestia stephenseni Paramysis kosswigi, Idotea baltica basteri, Idotea hectica, Sphaeroma serratum, Palaemon adspersus, Crangon crangon, Potamon ibericum tauricum and Carcinus aestuarii in the studied area. Potamon ibericum tauricum is the most encountered and widespread species. Key words: Freshwater, brackish water, Malacostraca, Sinop, Samsun, Turkey Introduction The Malacostraca is the largest subgroup of crustaceans and includes the decapods such as crabs, mole crabs, lobsters, true shrimps and the stomatopods or mantis shrimps. There are more than 22,000 taxa in this group representing two third of all crustacean species and contains all the larger forms. *Corresponding author: [email protected] 47 Malacostracans play an important role in aquatic ecosystems and therefore their conservation is important.
    [Show full text]
  • Molecular Data Suggest Multiple Origins and Diversification Times Of
    www.nature.com/scientificreports OPEN Molecular data suggest multiple origins and diversifcation times of freshwater gammarids on the Aegean archipelago Kamil Hupało1,3*, Ioannis Karaouzas2, Tomasz Mamos1,4 & Michał Grabowski1 Our main aim was to investigate the diversity, origin and biogeographical afliations of freshwater gammarids inhabiting the Aegean Islands by analysing their mtDNA and nDNA polymorphism, thereby providing the frst insight into the phylogeography of the Aegean freshwater gammarid fauna. The study material was collected from Samothraki, Lesbos, Skyros, Evia, Andros, Tinos and Serifos islands as well as from mainland Greece. The DNA extracted was used for amplifcation of two mitochondrial (COI and 16S) and two nuclear markers (28S and EF1-alpha). The multimarker time- calibrated phylogeny supports multiple origins and diferent diversifcation times for the studied taxa. Three of the sampled insular populations most probably represent new, distinct species as supported by all the delimitation methods used in our study. Our results show that the evolution of freshwater taxa is associated with the geological history of the Aegean Basin. The biogeographic afliations of the studied insular taxa indicate its continental origin, as well as the importance of the land fragmentation and the historical land connections of the islands. Based on the fndings, we highlight the importance of studying insular freshwater biota to better understand diversifcation mechanisms in fresh waters as well as the origin of studied Aegean freshwater taxa. Te Mediterranean islands are considered natural laboratories of evolution, exhibiting high levels of diversity and endemism, making them a vital part of one of the globally most precious biodiversity hotspots and a model system for studies of biogeography and evolution1–4.
    [Show full text]
  • Establishing Realistic Test Settings in Aquatic Ecotoxicological Risk Assessments Mona Katharina Feiner
    TECHNISCHE UNIVERSITÄT MÜNCHEN Lehrstuhl für Aquatische Systembiologie Establishing realistic test settings in aquatic ecotoxicological risk assessments Mona Katharina Feiner Vollständiger Abdruck der von der Fakultät Wissenschaftszentrum Weihenstephan für Ernährung, Landnutzung und Umwelt der Technischen Universität München zur Erlangung des akademischen Grades eines Doktors der Naturwissenschaften genehmigten Dissertation. Vorsitzender: Prof. Dr. Johannes Kollmann Prüfer der Dissertation: 1. Prof. Dr. Jürgen Geist 2. Prof. Dr. Christian Laforsch Die Dissertation wurde am 23.03.2017 bei der Technischen Universität München eingereicht und durch die Fakultät Wissenschaftszentrum Weihenstephan für Ernährung, Landnutzung und Umwelt am 28.09.2017 angenommen. Table of Content LIST OF TABLES ................................................................................................................................... 5 LIST OF FIGURES .................................................................................................................................. 6 PREFACE ................................................................................................................................................ 8 ABSTRACT ............................................................................................................................................. 9 ZUSAMMENFASSUNG .......................................................................................................................... 11 1. GENERAL INTRODUCTION .......................................................................................
    [Show full text]
  • Effects of the Acanthocephalan Polymorphus Minutus And
    EVects of the acanthocephalan Polymorphus minutus and the microsporidian Dictyocoela duebenum on energy reserves and stress response of cadmium exposed Gammarus fossarum Hui-Yu Chen1,2, ∗, Daniel S. Grabner2,∗, Milen Nachev2, Hsiu-Hui Shih1 and Bernd Sures2,3 1 Department of Life Science, National Taiwan University, Taipei, Taiwan 2 Aquatic Ecology and Centre for Water and Environmental Research, University of Duisburg–Essen, Essen, Germany 3 Department of Zoology, University of Johannesburg, Johannesburg, South Africa ∗ These authors contributed equally to this work. ABSTRACT Amphipods are commonly parasitized by acanthocephalans and microsporidians and co-infections are found frequently. Both groups of parasites are known to have severe eVects on their host. For example, microsporidians can modify host sex ratio and acanthocephalans can manipulate the behavior of the amphipod to promote transmission to the final host. TheseV e ects influence host metabolism in general and will also aVect the ability of amphipods to cope with additional stressors such as environmental pollution, e.g., by toxic metals. Here we tested the eVects of sub-lethal concentrations of cadmium on glycogen and lipid levels, as well as on the 70kDa heat shock protein (hsp70) response of field collected Gammarus fossarum, which were naturally infected with microsporidians and the acanthocephalan Polymorphus minutus. Infected and uninfected G. fossarum were exposed to a Submitted 13 August 2015 nominal Cd concentration of 4 µg/L, which resembled measured aqueous Cd ◦ Accepted 6 October 2015 concentration of 2.9 µg/L in reconstituted water for 7 d at 15 C in parallel to an Published 29 October 2015 unexposed control.
    [Show full text]
  • Gammarus Spp. in Aquatic Ecotoxicology and Water Quality Assessment: Toward Integrated Multilevel Tests
    Gammarus spp. in Aquatic Ecotoxicology and Water Quality Assessment: Toward Integrated Multilevel Tests Petra Y. Kunz, Cornelia Kienle, and Almut Gerhardt Contents 1 Introduction ................................. 2 2 Culturing of Gammarids ............................ 5 3 Gammarids in Lethality Testing ......................... 7 3.1 Pesticides, Metals, and Surfactants ..................... 7 3.2 Extracted, Fractionated Sediments ..................... 8 3.3 Coastal Sediment Toxicity ......................... 8 4 Feeding Activity ............................... 10 4.1 Time–Response Feeding Assays ...................... 10 4.2 Food Choice Experiments ......................... 16 4.3 Leaf-Mass Feeding Assays Linked to Food Consumption ........... 17 4.4 Modeling of Feeding Activity and Rate ................... 19 4.5 Post-exposure Feeding Depression Assay .................. 20 4.6 Effects of Parasites on Gammarid Feeding Ecology ............. 21 5Behavior................................... 22 5.1 Antipredator Behavior .......................... 22 5.2 Multispecies Freshwater BiomonitorR (MFB) ................ 27 5.3 A Sublethal Pollution Bioassay with Pleopod Beat Frequency and Swimming Endurance ........................... 29 5.4 Behavior in Combination with Other Endpoints ............... 29 6 Mode-of-Action Studies and Biomarkers .................... 31 6.1 Bioenergetic Responses, Excretion Rate and Respiration Rate ......... 32 6.2 Population Experiments, and Development and Reproduction Modeling .... 41 6.3 Endpoints and Biomarkers for
    [Show full text]
  • Distribution Patterns of Amphipods and Their Microsporidian Parasites in the Ruhr Metropolis, Germany Daniel S
    Grabner et al. Parasites & Vectors (2015) 8:419 DOI 10.1186/s13071-015-1036-6 RESEARCH Open Access Invaders, natives and their enemies: distribution patterns of amphipods and their microsporidian parasites in the Ruhr Metropolis, Germany Daniel S. Grabner1,5*†, Alexander M. Weigand2*†, Florian Leese2,4,5, Caroline Winking1, Daniel Hering1,5, Ralph Tollrian2,5 and Bernd Sures1,3,5 Abstract Background: The amphipod and microsporidian diversity in freshwaters of a heterogeneous urban region in Germany was assessed. Indigenous and non-indigenous host species provide an ideal framework to test general hypotheses on potentially new host-parasite interactions, parasite spillback and spillover in recently invaded urban freshwater communities. Methods: Amphipods were sampled in 17 smaller and larger streams belonging to catchments of the four major rivers in the Ruhr Metropolis (Emscher, Lippe, Ruhr, Rhine), including sites invaded and not invaded by non-indigenous amphipods. Species were identified morphologically (hosts only) and via DNA barcoding (hosts and parasites). Prevalence was obtained by newly designed parasite-specific PCR assays. Results: Three indigenous and five non-indigenous amphipod species were detected. Gammarus pulex was further distinguished into three clades (C, D and E) and G. fossarum more precisely identified as type B. Ten microsporidian lineages were detected, including two new isolates (designated as Microsporidium sp. nov. RR1 and RR2). All microsporidians occurred in at least two different host clades or species. Seven genetically distinct microsporidians were present in non-invaded populations, six of those were also found in invaded assemblages. Only Cucumispora dikerogammari and Dictyocoela berillonum can be unambiguously considered as non-indigenous co-introduced parasites.
    [Show full text]
  • Ecology of Ontogenetic Body-Mass Scaling of Gill Surface Area in a Freshwater Crustacean Douglas S
    © 2017. Published by The Company of Biologists Ltd | Journal of Experimental Biology (2017) 220, 2120-2127 doi:10.1242/jeb.155242 RESEARCH ARTICLE Ecology of ontogenetic body-mass scaling of gill surface area in a freshwater crustacean Douglas S. Glazier1,* and David A. Paul2 ABSTRACT This equation describes a linear relationship in log–log space, where Several studies have documented ecological effects on intraspecific R is metabolic rate, a is the scaling coefficient (antilog of the and interspecific body-size scaling of metabolic rate. However, little is intercept of the log-linear regression line), M is body mass and b is known about how various ecological factors may affect the scaling of the scaling exponent (slope of the log-linear regression line). For respiratory structures supporting oxygen uptake for metabolism. To our decades, the scaling exponent was thought to be 3/4 or ‘ ’ knowledge, our study is the first to provide evidence for ecological approximately so, hence the proclamation of a 3/4-power law effects on the scaling of a respiratory structure among conspecific (Kleiber, 1932, 1961; Schmidt-Nielsen, 1984; Savage et al., 2004). populations of any animal. We compared the body-mass scaling of gill Furthermore, this law has been explained as being the result of surface area (SA) among eight spring-dwelling populations of the resource (oxygen and nutrient) supply constraints, in particular amphipod crustacean Gammarus minus. Although gill SA scaling was those arising from the geometry and physics of internal resource- not related to water temperature, conductivity or G. minus population transport networks (West et al., 1997; Banavar et al., 2010, 2014).
    [Show full text]
  • Freshwater Gammarus Species from Europe, North Africa and Adjacent Regions of Asia (Crustacea-Amphipoda)
    FRESHWATER GAMMARUS SPECIES FROM EUROPE, NORTH AFRICA AND ADJACENT REGIONS OF ASIA (CRUSTACEA-AMPHIPODA) PART I. GAMMARUS PULEX-GROUP AND RELATED SPECIES by GORDAN S. KARAMAN Biological Institute, Titograd, Yugoslavia & SJOUK PINKSTER Institute of Taxonomic Zoology, University of Amsterdam, The Netherlands FRESHWATER GAMMARUS SPECIES FROM EUROPE, NORTH AFRICA AND ADJACENT REGIONS OF ASIA (CRIJSTACEA-AMPHIPODA) PART I. GAMMARUS PULEX-GROUP AND RELATED SPECIES by GORDAN S. KARAMAN Biological Institute, Titograd, Yugoslavia SJOUK PINKSTER Institute of Taxonomic Zoology, University of Amsterdam, The Netherlands ABSTRACT 10) Within some taxa (e.g. G. fossarum and G. p. pulex) morphologically aberrant populations can be found. Since these 1) Within the genus Gammarus s.str., which is widely distrib- populations do successfully cross-breed and are sympatric they uted throughout the northern hemisphere, more than 100 must be considered mere variations. freshwater species can be distinguished. 11) We had serious problems to determine the identity 2) These freshwater species can be classified in three of several Gammarus species, especially from Asia Minor, artificial groups: (a) the G. pulex-group (species without because of the impossibility to obtain literature and type dorsal carina and with dense setation on pereiopods 3 and 4 material of some Russian authors. (So we cannot exclude the and uropod 3), (b) the G. balcanicus-group (species without possibility that our species described from Asia might be dorsal carina and poorly setose pereiopods 3 and 4 and identical with a species formerly described by a Russian uropod 3) and (c) the G. roeseli-group (species with dorsal author). carina). These groups are merely artificial ones since tran- 12) For all species, except the most common ones, com- sitive (intermediate) species do exist.
    [Show full text]
  • The Aquatic Amphipoda and Isopoda (Crustacea) of the Transdanubian Mountains in Northwest Hungary
    ©Erik Mauch Verlag, Dinkelscherben, Deutschland,73 Download unter www.biologiezentrum.at Lauterbornia 49: 73-76, D-86424 Dinkelscherben, 2004-05-20 The aquatic Amphipoda and Isopoda (Crustacea) of the Transdanubian Mountains in Northwest Hungary Jenö Kontschan With 1 Figure and 1 Table Keywords: Amphipoda, Isopoda, Crustacea, Transdanubian Mountains, Hungary, faunistics Schlagwörter: Amphipoda, Isopoda, Crustacea,Transdanubisches Gebirge, Ungarn, Faunistik The examination of springs, streams and ponds in the Transdanubian Mountains yielded 4 Amphipoda species (Gammarus roeselii, Gammarus fossarum, Synurella ambulans, Niphargus valacbicus) and the Isopoda species Asellus aquaticus. Most common was Gammarus roeselii; Asellus aquaticus was frequent in waters with high content of organic matter. 1 Introduction The aquatic Peracarida fauna of Hungary consists of 27 Amphipoda (Musko 1994), 6 Isopoda and 1 Mysidacea species. 13 Amphipoda species live in subter­ ranean waters, 6 in surface waters (springs, streams, ponds), 6 in the large rivers Danube and Tisza and the lake Balaton, and 2 are terrestrial. About the Am­ phipoda and aquatic Isopoda of the Transdanubian Mountains is little known as well as in the most regions of Hungary (Musko 1994). There are some data from the Pilis (Csörgits 2000), Gerecse, Vertes (Kontschan 2000a, 2001a) and the region of Bakony (Dudich 1927, Kontschan 2000b, Lukacsovics 1958, Po- nyi & al. 2000, 2001, Stiller 1957). 2 Sampling sites and methods The Gerecse and Vertes (west of Budapest) and the region of Bakony (north of the Balaton) constitute the main range of the Transdanubian Mountains (Fig. 1.); this area is dry and poor in streams and springs. Most of the springs are limnocrenes, the streams are usually silt-bedded and slowly flowing.
    [Show full text]
  • Life History and Reproductive Capacity of Gammarus Fossarum and G. Roeseli (Crustacea: Amphipoda) Under Naturally fluctuating Water Temperatures: a Simulation Study
    Freshwater Biology (2003) 48, 53–66 Life history and reproductive capacity of Gammarus fossarum and G. roeseli (Crustacea: Amphipoda) under naturally fluctuating water temperatures: a simulation study MANFRED PO¨ CKL,* BRUCE W. WEBB† and DAVID W. SUTCLIFFE‡ *Institute of Ecology and Conservation Biology, Department of Limnology, University of Vienna, and State Government of Lower Austria, Experts for the Conservation of Nature, Landhausplatz, St Po¨lten, Austria †School of Geography and Archaeology, University of Exeter, Amory Building, Rennes Drive, Exeter, U.K. ‡The Freshwater Biological Association, The Ferry House, Far Sawrey, Ambleside, Cumbria, U.K. SUMMARY 1. Mathematical functions developed in long-term laboratory experiments at different constant temperatures were combined with daily water temperatures for 1991–93 in eight Austrian streams and rivers to simulate the complex life histories and reproductive capacities of two freshwater amphipods: Gammarus fossarum and G. roeseli. The functions describe brood development times, hatching success, times taken to reach sexual maturity, growth, and fecundity. The sex ratio was assumed to be 0.5 and an autumn–winter reproductive resting period was based on observations of six river populations. Simulations included summer-cold mountain streams, summer-warm lowland rivers, watercourses fed by groundwater or influenced by heated effluents, and varying amplitudes of change within each year. 2. A FORTRAN 77 computer program calculated growth from birth to sexual maturity of first-generation females born on the first day of each calendar month in 1991, and the numbers of offspring successfully released from the maternal broodpouch in successive broods. At the 1991–93 regimes of temperature, individual G.
    [Show full text]