Feeding Ecology of European Flounder, Platichthys Flesus, in the Lima Estuary (Nw
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Aspects of the Life History of Hornyhead Turbot, Pleuronichthys Verticalis, Off Southern California
Aspects of the Life History of Hornyhead Turbot, Pleuronichthys verticalis, off Southern California he hornyhead turbot T(Pleuronichthys verticalis) is a common resident flatfish on the mainland shelf from Magdalena Bay, Baja Califor- nia, Mexico to Point Reyes, California (Miller and Lea 1972). They are randomly distributed over the bottom at a density of about one fish per 130 m2 and lie partially buried in the sediment (Luckinbill 1969). Hornyhead turbot feed primarily on sedentary, tube-dwelling polychaetes (Luckinbill 1969, Allen 1982, Cross et al. 1985). They pull the tubes from the sediment, Histological section of a fish ovary. extract the polychaete, and then eject the tube (Luckinbill 1969). Hornyhead turbot are Orange County, p,p’-DDE Despite the importance of batch spawners and may averaged 362 μg/kg wet the hornyhead turbot in local spawn year round (Goldberg weight in hornyhead turbot monitoring programs, its life 1982). Their planktonic eggs liver and 5 μg/kg dry weight in history has received little are 1.00-1.16 mm diameter the sediments (CSDOC 1992). attention. The long-term goal (Sumida et al. 1979). Their In the same year in Santa of our work is to determine larvae occur in the nearshore Monica Bay, p,p’-DDE aver- how a relatively low trophic plankton throughout the year aged 7.8 mg/kg wet weight in level fish like the hornyhead (Gruber et al. 1982, Barnett et liver and 81 μg/kg dry weight turbot accumulates tissue al. 1984, Moser et al. 1993). in the sediments (City of Los levels of chlorinated hydrocar- Several agencies in South- Angeles 1992). -
The Influence of Hediste Diversicolor (O.F
Rostock. Meeresbiolog. Beitr. (1993)1 Andreas Bick; Günter Arlt The influence of Hediste diversicolor (O.F. MÜLLER, 1776) on the macro- and meiozoobenthos of a shallow water area of Mecklenburg Bay (Western Baltic Sea) Introduction The purpose of many ecological studies is to identify interactions between faunistic ecosystem components by means of laboratory and field experiments. It has often been shown that abiotic and biotic factors such as competition, disturbance and predation influence the composition and dynamics of macrobenthos communities (REISE, 1977; COMMITO and AMBROSE, 1985; AM- BROSE, 1986; BEUKEMA, 1987; KIKUCHI, 1987; REDMOND and SCOTT, 1989; COMMITO and BANCAVAGE, 1989; MATILA and BONSDORFF, 1989; HILL et al., 1990). Experiments have also been performed to detect interactions between macrofauna and meiofauna (BELL & Coull, 1978; REISE, 1979; GEE et al., 1985; ALONGI and TENORE, 1985). The interactions between Nereidae and infauna that are common in shallow water and are fairly easily handled have been a major topic of study (COMMITO, 1982; REISE, 1979b; COMMITO and SCHRADER, 1985; OLAFSON and PERSSON 1986; RÖNN et al., 1988). The purpose of our studies was to investigate the influence of the omnivorous H. diversicolor on the infauna of a shallow water region in the southern Baltic Sea. H. diversicolor achieves abun- dances of between 5,000 and 15,000 ind m"2 (individual dominances up to 15 %) in the investi- gation area and is thus a major component of the macrofauna. It therefore seemed likely that its carnivorous feeding habits can affect community structure. To detect direct influences on both the macrozoobenthos and meiozoobenthos and to reduce box effects, we performed short term experiments. -
The State of Mediterranean and Black Sea Fisheries 2018
Food and Agriculture General Fisheries Commission for the Mediterranean Organization of the Commission générale des pêches United Nations pour la Méditerranée ISSN 2413-6905 THE STATE OF MEDITERRANEAN AND BLACK SEA FISHERIES 2018 Reference: FAO. 2018. The State of Mediterranean and Black Sea Fisheries General Fisheries Commission for the Mediterranean. Rome, Italy. pp. 164. THE STATE OF MEDITERRANEAN AND BLACK SEA FISHERIES 2018 FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS Rome, 2018 Required citation: FAO. 2018. The State of Mediterranean and Black Sea Fisheries. General Fisheries Commission for the Mediterranean. Rome. 172 pp. 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 specifc 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 refect the views or policies of FAO. ISBN 978-92-5-131152-3 © FAO, 2018 Some rights reserved. This work is made available under the Creative Commons Attribution-NonCommercial-ShareAlike 3.0 IGO licence (CC BY-NC-SA 3.0 IGO; https://creativecommons.org/licenses/by-nc-sa/3.0/igo/legalcode/legalcode). -
Passarelli Et Al 2012.Pdf
Journal of Experimental Marine Biology and Ecology 438 (2012) 52–60 Contents lists available at SciVerse ScienceDirect Journal of Experimental Marine Biology and Ecology journal homepage: www.elsevier.com/locate/jembe Surface adhesion of microphytobenthic biofilms is enhanced under Hediste diversicolor (O.F. Müller) trophic pressure Claire Passarelli ⁎, Cédric Hubas, Audrey Nicolas Segui, Julie Grange, Tarik Meziane UMR BOREA-CNRS 7208,Muséum National d'Histoire Naturelle, CP 53, 61 rue Buffon, F-75231 Paris Cedex 05, France article info abstract Article history: In soft-bottom tidal flats, sediment stability is one of the crucial parameters modulating the abundance and com- Received 16 July 2012 position of benthic assemblages. It is dependent on a wide range of variables, both abiotic and biotic. Investigat- Received in revised form 1 October 2012 ing how these variables and their interactions influence sediment stability is therefore essential to understand Accepted 7 October 2012 how benthic assemblages are distributed in their environment. In this context, we designed a microcosm Available online xxxx study to examine how microorganisms and macrofauna interact to alter sediment stability. We cultured a natural microbial community, enriched with diatoms, both alone and together with the common ragworm Hediste Keywords: Diatoms diversicolor, and monitored their effects on photosynthetic biomasses, bacterial abundances, exopolymer secre- Extracellular polymeric substances (EPS) tions and sediment stability. We also assessed the consumption of biofilm by worms using fatty acid biomarkers. Fatty acids Our results demonstrate that even if H. diversicolor fed on diatoms, they stimulated biofilm development, H. diversicolor in terms of photosynthetic biomass and exopolymer production. Also, sediment cohesiveness was enhanced Microphytobenthos when both diatoms and H. -
New Zealand Fishes a Field Guide to Common Species Caught by Bottom, Midwater, and Surface Fishing Cover Photos: Top – Kingfish (Seriola Lalandi), Malcolm Francis
New Zealand fishes A field guide to common species caught by bottom, midwater, and surface fishing Cover photos: Top – Kingfish (Seriola lalandi), Malcolm Francis. Top left – Snapper (Chrysophrys auratus), Malcolm Francis. Centre – Catch of hoki (Macruronus novaezelandiae), Neil Bagley (NIWA). Bottom left – Jack mackerel (Trachurus sp.), Malcolm Francis. Bottom – Orange roughy (Hoplostethus atlanticus), NIWA. New Zealand fishes A field guide to common species caught by bottom, midwater, and surface fishing New Zealand Aquatic Environment and Biodiversity Report No: 208 Prepared for Fisheries New Zealand by P. J. McMillan M. P. Francis G. D. James L. J. Paul P. Marriott E. J. Mackay B. A. Wood D. W. Stevens L. H. Griggs S. J. Baird C. D. Roberts‡ A. L. Stewart‡ C. D. Struthers‡ J. E. Robbins NIWA, Private Bag 14901, Wellington 6241 ‡ Museum of New Zealand Te Papa Tongarewa, PO Box 467, Wellington, 6011Wellington ISSN 1176-9440 (print) ISSN 1179-6480 (online) ISBN 978-1-98-859425-5 (print) ISBN 978-1-98-859426-2 (online) 2019 Disclaimer While every effort was made to ensure the information in this publication is accurate, Fisheries New Zealand does not accept any responsibility or liability for error of fact, omission, interpretation or opinion that may be present, nor for the consequences of any decisions based on this information. Requests for further copies should be directed to: Publications Logistics Officer Ministry for Primary Industries PO Box 2526 WELLINGTON 6140 Email: [email protected] Telephone: 0800 00 83 33 Facsimile: 04-894 0300 This publication is also available on the Ministry for Primary Industries website at http://www.mpi.govt.nz/news-and-resources/publications/ A higher resolution (larger) PDF of this guide is also available by application to: [email protected] Citation: McMillan, P.J.; Francis, M.P.; James, G.D.; Paul, L.J.; Marriott, P.; Mackay, E.; Wood, B.A.; Stevens, D.W.; Griggs, L.H.; Baird, S.J.; Roberts, C.D.; Stewart, A.L.; Struthers, C.D.; Robbins, J.E. -
OREGON ESTUARINE INVERTEBRATES an Illustrated Guide to the Common and Important Invertebrate Animals
OREGON ESTUARINE INVERTEBRATES An Illustrated Guide to the Common and Important Invertebrate Animals By Paul Rudy, Jr. Lynn Hay Rudy Oregon Institute of Marine Biology University of Oregon Charleston, Oregon 97420 Contract No. 79-111 Project Officer Jay F. Watson U.S. Fish and Wildlife Service 500 N.E. Multnomah Street Portland, Oregon 97232 Performed for National Coastal Ecosystems Team Office of Biological Services Fish and Wildlife Service U.S. Department of Interior Washington, D.C. 20240 Table of Contents Introduction CNIDARIA Hydrozoa Aequorea aequorea ................................................................ 6 Obelia longissima .................................................................. 8 Polyorchis penicillatus 10 Tubularia crocea ................................................................. 12 Anthozoa Anthopleura artemisia ................................. 14 Anthopleura elegantissima .................................................. 16 Haliplanella luciae .................................................................. 18 Nematostella vectensis ......................................................... 20 Metridium senile .................................................................... 22 NEMERTEA Amphiporus imparispinosus ................................................ 24 Carinoma mutabilis ................................................................ 26 Cerebratulus californiensis .................................................. 28 Lineus ruber ......................................................................... -
Recycled Fish Sculpture (.PDF)
Recycled Fish Sculpture Name:__________ Fish: are a paraphyletic group of organisms that consist of all gill-bearing aquatic vertebrate animals that lack limbs with digits. At 32,000 species, fish exhibit greater species diversity than any other group of vertebrates. Sculpture: is three-dimensional artwork created by shaping or combining hard materials—typically stone such as marble—or metal, glass, or wood. Softer ("plastic") materials can also be used, such as clay, textiles, plastics, polymers and softer metals. They may be assembled such as by welding or gluing or by firing, molded or cast. Researched Photo Source: Alaskan Rainbow STEP ONE: CHOOSE one fish from the attached Fish Names list. Trout STEP TWO: RESEARCH on-line and complete the attached K/U Fish Research Sheet. STEP THREE: DRAW 3 conceptual sketches with colour pencil crayons of possible visual images that represent your researched fish. STEP FOUR: Once your fish designs are approved by the teacher, DRAW a representational outline of your fish on the 18 x24 and then add VALUE and COLOUR . CONSIDER: Individual shapes and forms for the various parts you will cut out of recycled pop aluminum cans (such as individual scales, gills, fins etc.) STEP FIVE: CUT OUT using scissors the various individual sections of your chosen fish from recycled pop aluminum cans. OVERLAY them on top of your 18 x 24 Representational Outline 18 x 24 Drawing representational drawing to judge the shape and size of each piece. STEP SIX: Once you have cut out all your shapes and forms, GLUE the various pieces together with a glue gun. -
(Hediste) Diversicolor (Müller, 1776) to Potential Fish Predation
Smelling Danger – Alarm Cue Responses in the Polychaete Nereis (Hediste) diversicolor (Müller, 1776) to Potential Fish Predation C. Elisa Schaum¤, Robert Batty, Kim S. Last* Scottish Association of Marine Science, Scottish Marine Institute, Dunstaffnage, Scotland Abstract The harbour ragworm, Nereis (Hediste) diversicolor is a common intertidal marine polychaete that lives in burrows from which it has to partially emerge in order to forage. In doing so, it is exposed to a variety of predators. One way in which predation risk can be minimised is through chemical detection from within the relative safety of the burrows. Using CCTV and motion capture software, we show that H. diversicolor is able to detect chemical cues associated with the presence of juvenile flounder (Platichthys flesus). Number of emergences, emergence duration and distance from burrow entrance are all significantly reduced during exposure to flounder conditioned seawater and flounder mucous spiked seawater above a threshold with no evidence of behavioural habituation. Mucous from bottom- dwelling juvenile plaice (Pleuronectes platessa) and pelagic adult herring (Clupea harengus) elicit similar responses, suggesting that the behavioural reactions are species independent. The data implies that H. diversicolor must have well developed chemosensory mechanisms for predator detection and is consequently able to effectively minimize risk. Citation: Schaum CE, Batty R, Last KS (2013) Smelling Danger – Alarm Cue Responses in the Polychaete Nereis (Hediste) diversicolor (Müller, 1776) to Potential Fish Predation. PLoS ONE 8(10): e77431. doi:10.1371/journal.pone.0077431 Editor: Roberto Pronzato, University of Genova, Italy, Italy Received June 10, 2013; Accepted September 2, 2013; Published October 14, 2013 Copyright: © 2013 Schaum et al. -
Burial of Zostera Marina Seeds in Sediment Inhabited by Three Polychaetes: Laboratory and field Studies
Journal of Sea Research 71 (2012) 41–49 Contents lists available at SciVerse ScienceDirect Journal of Sea Research journal homepage: www.elsevier.com/locate/seares Burial of Zostera marina seeds in sediment inhabited by three polychaetes: Laboratory and field studies M. Delefosse ⁎, E. Kristensen Institute of Biology, University of Southern Denmark, Campusvej 55, 5230 Odense M, Denmark article info abstract Article history: The large number of seeds produced by eelgrass, Zostera marina, provides this plant with a potential to disperse Received 4 December 2011 widely and colonise new areas. After dispersal, seeds must be buried into sediment for assuring long-term survival, Received in revised form 25 April 2012 successful germination and safe seedling development. Seeds may be buried passively by sedimentation or actively Accepted 25 April 2012 through sediment reworking by benthic fauna. We evaluated the effect of three polychaetes on the burial rate and Available online 5 May 2012 depth of eelgrass seeds. Burial was first measured in controlled laboratory experiments using different densities of Nereis (Hediste) diversicolor (400–3200 ind m−2), Arenicola marina (20–80 ind m−2), and the invasive Marenzelleria Keywords: – −2 Polychaete viridis (400 1600 ind m ). The obtained results were subsequently compared with burial rates of seed mimics in 2 Ecosystem engineer experimental field plots (1 m ) dominated by the respective polychaetes. High recovery of seeds in the laboratory Invasive species (97–100%) suggested that none of these polychaetes species feed on eelgrass seeds. N. diversicolor transported Zostera marina seeds rapidly (b1 day) into its burrow, where they remained buried at a median depth of 0.5 cm. -
2017 Gulf of Alaska Bottom Trawl Survey
NOAA Technical Memorandum NMFS-AFSC-374 doi:10.7289/V5/TM-AFSC-374 Data Report: 2017 Gulf of Alaska Bottom Trawl Survey P. G. von Szalay and N. W. Raring U.S. DEPARTMENT OF COMMERCE National Oceanic and Atmospheric Administration National Marine Fisheries Service Alaska Fisheries Science Center March 2018 NOAA Technical Memorandum NMFS The National Marine Fisheries Service's Alaska Fisheries Science Center uses the NOAA Technical Memorandum series to issue informal scientific and technical publications when complete formal review and editorial processing are not appropriate or feasible. Documents within this series reflect sound professional work and may be referenced in the formal scientific and technical literature. The NMFS-AFSC Technical Memorandum series of the Alaska Fisheries Science Center continues the NMFS-F/NWC series established in 1970 by the Northwest Fisheries Center. The NMFS-NWFSC series is currently used by the Northwest Fisheries Science Center. This document should be cited as follows: von Szalay, P. G., and N. W. Raring. 2018. Data Report: 2017 Gulf of Alaska bottom trawl survey. U.S. Dep. Commer., NOAA Tech. Memo. NMFS-AFSC-374, 260 p. Document available: http://www.afsc.noaa.gov/Publications/AFSC-TM/NOAA-TM-AFSC-374.pdf Reference in this document to trade names does not imply endorsement by the National Marine Fisheries Service, NOAA. NOAA Technical Memorandum NMFS-AFSC-374 doi:10.7289/V5/TM-AFSC-374 Data Report: 2017 Gulf of Alaska Bottom Trawl Survey P. G. von Szalay and N. W. Raring Resource Assessment and Conservation Engineering Division Alaska Fisheries Science Center National Marine Fisheries Service National Oceanic and Atmospheric Administration 7600 Sand Point Way N.E. -
Essential Fish Habitat (EFH) Assessment Gloucester Harbor, Massachusetts December 2001
Essential Fish Habitat (EFH) Assessment Gloucester Harbor, Massachusetts December 2001 Prepared for: Massachusetts Office of Coastal Zone Management 251 Causeway Street, Suite 900 Boston, MA 02114-2119 Prepared by: Maguire Group Inc. 225 Foxborough Boulevard Foxborough, MA 02035 508-543-1700 Table of Contents TABLE OF CONTENTS 1.0 INTRODUCTION 1-1 1.1 Purpose 1-1 1.2 Description of the Study Area 1-2 1.3 EFH Designation Areas 1-6 1.4 Existing Marine Fish Community of Gloucester Harbor 1-9 1.4.1 Summary of Jerome et al, 1969 Surveys 1-9 1.4.2 Summary of NAI Results 1-10 1.4.2.1 Shore Surveys 1-10 1.4.2.2 Offshore Survey 1-11 2.0 ESSENTIAL MARINE FISH HABITAT DESCRIPTIONS 2-1 2.1 American Plaice 2-1 2.2 Atlantic Cod 2-2 2.3 Atlantic Halibut 2-3 2.4 Atlantic Herring 2-3 2.5 Atlantic Mackerel 2-4 2.6 Atlantic Sea Scallop 2-5 2.7 Black Sea Bass 2-5 2.8 Bluefish 2-6 2.9 Haddock 2-6 2.10 Short-finned Squid 2-6 2.11 Long-finned Squid 2-7 2.12 Monkfish 2-7 2.13 Ocean Pout 2-8 2.14 Pollock 2-8 2.15 Red Hake 2-9 2.16 Redfish 2-10 2.17 Scup 2-11 2.18 Summer Flounder 2-11 2.19 Surf Clam 2-11 2.20 White Hake 2-12 2.21 Whiting 2-12 2.22 Windowpane Flounder 2-13 2.23 Winter Flounder 2-14 2.24 Witch Flounder 2-14 2.25 Yellowtail Flounder 2-15 2.26 Ocean Quahog 2-16 3.0 DREDGING IMPACTS TO FISH AND EFH 3-1 3.1 Impairment of Water Quality 3-1 Essential Fish Habitat Assessment – Gloucester Harbor, MA Table of Contents 3.1.1 Physical Impairment 3-1 3.1.2 Chemical Impairment 3-1 3.1.3 Biological Impairment 3-6 3.2 Destruction of Benthic Habitat 3-6 3.2.1 Direct -
Intrinsic Vulnerability in the Global Fish Catch
The following appendix accompanies the article Intrinsic vulnerability in the global fish catch William W. L. Cheung1,*, Reg Watson1, Telmo Morato1,2, Tony J. Pitcher1, Daniel Pauly1 1Fisheries Centre, The University of British Columbia, Aquatic Ecosystems Research Laboratory (AERL), 2202 Main Mall, Vancouver, British Columbia V6T 1Z4, Canada 2Departamento de Oceanografia e Pescas, Universidade dos Açores, 9901-862 Horta, Portugal *Email: [email protected] Marine Ecology Progress Series 333:1–12 (2007) Appendix 1. Intrinsic vulnerability index of fish taxa represented in the global catch, based on the Sea Around Us database (www.seaaroundus.org) Taxonomic Intrinsic level Taxon Common name vulnerability Family Pristidae Sawfishes 88 Squatinidae Angel sharks 80 Anarhichadidae Wolffishes 78 Carcharhinidae Requiem sharks 77 Sphyrnidae Hammerhead, bonnethead, scoophead shark 77 Macrouridae Grenadiers or rattails 75 Rajidae Skates 72 Alepocephalidae Slickheads 71 Lophiidae Goosefishes 70 Torpedinidae Electric rays 68 Belonidae Needlefishes 67 Emmelichthyidae Rovers 66 Nototheniidae Cod icefishes 65 Ophidiidae Cusk-eels 65 Trachichthyidae Slimeheads 64 Channichthyidae Crocodile icefishes 63 Myliobatidae Eagle and manta rays 63 Squalidae Dogfish sharks 62 Congridae Conger and garden eels 60 Serranidae Sea basses: groupers and fairy basslets 60 Exocoetidae Flyingfishes 59 Malacanthidae Tilefishes 58 Scorpaenidae Scorpionfishes or rockfishes 58 Polynemidae Threadfins 56 Triakidae Houndsharks 56 Istiophoridae Billfishes 55 Petromyzontidae