To View Asset

Total Page:16

File Type:pdf, Size:1020Kb

To View Asset Baywide Monitoring of Key Fishery Species in Seagrass Beds Sub‐Program Progress Report No. 8 (November 2011) Julia Kent, Greg Jenkins and Neil Hutchinson January 2012 Fisheries Victoria Technical Report Series No. 159 If you would like to receive this Copyright The State of Victoria, Department of information/publication in an Primary Industries, 2012. accessible format (such as large This publication is copyright. No part may be reproduced by any process except in accordance print or audio) please call the with the provisions of the Copyright Act 1968. Customer Service Centre on: Authorised by the Victorian Government, GPO 136 186, TTY: 1800 122 969, Box 4440, Melbourne, VIC 3001 or email Printed by Fisheries Victoria, Queenscliff, [email protected] Victoria Published: Fisheries Victoria Kent, J., Jenkins, G., and Hutchinson, N. (2012). Department of Primary Baywide Monitoring of Key Fishery Species in Industries, Queenscliff Centre Seagrass Beds Sub‐Program. Progress Report No. PO Box 114, Queenscliff, Victoria 8 (November 2011). Fisheries Victoria Technical 3225 Australia. Report Series No. 159, January 2012. Fisheries Victoria, Department of Primary Industries, Queenscliff, Victoria, Australia. 10pp. General disclaimer This publication may be of assistance to you but the State of Victoria and its employees do not ISSN 1835‐4785 guarantee that the publication is without flaw of ISBN 978‐1‐74326‐096‐8 any kind or is wholly appropriate for your particular purposes and therefore disclaims all liability for any error, loss or other consequence which may arise from you relying on any information in this publication. Baywide Monitoring of Key Fishery Species in Seagrass Beds Progress Report #8 ii Table of Contents List of Tables ............................................................................................................................................................ iv List of Figures........................................................................................................................................................... iv Introduction............................................................................................................ 1 This Report..................................................................................................................................................................1 Materials and Methods......................................................................................... 2 Field and laboratory methods..................................................................................................................................2 Results and Discussion ........................................................................................ 3 Species Richness ........................................................................................................................................................3 Abundance ..................................................................................................................................................................3 Comparison with previous surveys........................................................................................................................3 Conclusion ..................................................................................................................................................................4 References ............................................................................................................... 5 Appendix 1 Summary Data ................................................................................. 6 Appendix 2............................................................................................................ 10 Raw data ....................................................................................................................................................................10 Data Files...................................................................................................................................................................10 Baywide Monitoring of Key Fishery Species in Seagrass Beds Progress Report #8 iii List of Tables Table 1. Average abundance (No. haul‐1; four hauls per site) of fish and squid sampled in deep and shallow seagrass beds at each site (Blairgowrie, Mud Islands and St Leonards) and total number of each species collected (species names from Gomon et al. (2008) and Museum of Victoria) in November 2011. Species not found during previous sampling events are marked in bold.................... 6 List of Figures Figure 1. CDBMP sampling sites for monitoring key fishery species in seagrass beds sub‐program. .......... 2 Figure 2. Average (+SE) species richness recorded in seagrass beds at each site in PPB from April 2008 to November 2011................................................................................................................................................... 8 Figure 3. Average (+SE) fish abundance (totalled for all species) recorded in seagrass beds at each site in PPB from April 2008 to November 2011 (NB scale change between graphs)............................................ 9 Baywide Monitoring of Key Fishery Species in Seagrass Beds Progress Report #8 iv Introduction The purpose of the Monitoring Key Fishery Species in Seagrass Beds Sub‐Program of the This Report Channel Deepening Baywide Monitoring This report summarises preliminary, qualitative Programs (CDBMP) for Port Phillip Bay (PPB) is results of the fourth spring survey (November to improve the understanding of the fish species 2011) for the sub‐program. using seagrass beds in the Bay. This sub‐ Length measurements recorded during program is described in the CDBMP Detailed November 2011, together with statistically Design: CDP_ENV_MD_018 Rev 2.1 (PoMC analysed results for the survey, will be reported 2009). in Milestone Report No. 8. The objective is to collect data on the types and abundance of fish in shallow and deeper seagrass beds that will fill existing knowledge gaps and assist in understanding the significance of any observed changes in seagrass habitat for these fish. Surveys are undertaken to compare the distribution and abundance of fish in shallow (< 1 m) and deeper (2–8 m) seagrass beds in three areas of PPB. These surveys are conducted in spring (November) and autumn (April) each year between 2008 and 2011. The autumn 2008, spring 2008, autumn 2009, spring 2009, autumn 2010, spring 2010 and autumn 2011 surveys were reported in Smith et al. (2008), Hutchinson et al. (2009a; b; 2010; 2011a; b) and Hutchinson and Jenkins (2010). Baywide Monitoring of Key Fishery Species in Seagrass Beds Progress Report #8 1 Materials and Methods Field and laboratory methods Field and laboratory methods utilised in the There were no significant field events observed. present study are described by Smith et al. (2008) No QA/QC issues were recorded during this and PoMC (2009). reporting period. During the spring 2011 study period (this report), fish were sampled in shallow (< 1 m) and deeper (2–8 m) seagrass, Heterozostera nigricaulis, beds at three sites: Blairgowrie, Mud Islands and St Leonards (Figure 1). Samples were collected between 31 October and 28 November 2011. Figure 1. CDBMP sampling sites for monitoring key fishery species in seagrass beds sub‐program. Baywide Monitoring of Key Fishery Species in Seagrass Beds Progress Report #8 2 Results and Discussion A total of 43 fish species (41 finfish, one ray and Leonards (299 fish), where abundances were one squid) from 24 families (22 families for lowest, spotted pipefish, wide‐body pipefish and finfish, one family for rays and one family for grass clingfish (Gobiesocidae Genus C sp.1) squid) were sampled for all sites. Summary data occurred in the greatest numbers. and plots for species richness and abundance at The abundance of fish (not including ray and all sites for the reporting period are provided in squid species; total for all sites) was higher in Appendix 1 (Table 1; Figs 2 and 3). Data files for shallow seagrass (3067 fish) than deep seagrass this reporting period are summarised in (466 fish). Shallow seagrass was dominated by Appendix 2. shortsnout hardyhead (1217 fish), blue sprat (629 Fish species sampled in November 2011 were fish) and smallmouth hardyhead (450 fish). indicative of those collected in and around Deep seagrass was dominated by a range of seagrass beds in previous surveys (Smith et al. species including bridled leatherjacket (147 fish), 2008; Hutchinson et al. 2009a; b; Hutchinson and little rock whiting (Neoodax balteatus; 63 fish), Jenkins 2010; Hutchinson et al. 2010; 2011a; b) spotted pipefish (56 fish) and grass clingfish (47 and in previous studies of PPB (Jenkins et al. fish). 1997; Hindell et al. 2001). Shortsnout hardyhead (Kestratherina brevirostris; atherinids), smallmouth hardyhead (Atherinosoma microstoma; atherinids), Comparison with previous blue sprat (Spratelloides robustus; clupeids), surveys spotted pipefish (Stigmatopora argus; During this survey, two species of fish were syngnathids), wide‐body pipefish (Stigmatopora sampled that were not found during the previous nigra; syngnathids) and bridled leatherjacket surveys: (Acanthaluteres spilomelanurus; monacanthids) were the dominant species. Velvetfish (Aploactisoma milesii; one fish) Silverbelly (Parequula melbournensis; one fish) Species Richness In contrast, 42 species of fish found in one or Species richness
Recommended publications
  • Download Full Article 1.0MB .Pdf File
    Memoirs of the Museum of Victoria 57( I): 143-165 ( 1998) 1 May 1998 https://doi.org/10.24199/j.mmv.1998.57.08 FISHES OF WILSONS PROMONTORY AND CORNER INLET, VICTORIA: COMPOSITION AND BIOGEOGRAPHIC AFFINITIES M. L. TURNER' AND M. D. NORMAN2 'Great Barrier Reef Marine Park Authority, PO Box 1379,Townsville, Qld 4810, Australia ([email protected]) 1Department of Zoology, University of Melbourne, Parkville, Vic. 3052, Australia (corresponding author: [email protected]) Abstract Turner, M.L. and Norman, M.D., 1998. Fishes of Wilsons Promontory and Comer Inlet. Victoria: composition and biogeographic affinities. Memoirs of the Museum of Victoria 57: 143-165. A diving survey of shallow-water marine fishes, primarily benthic reef fishes, was under­ taken around Wilsons Promontory and in Comer Inlet in 1987 and 1988. Shallow subtidal reefs in these regions are dominated by labrids, particularly Bluethroat Wrasse (Notolabrus tet­ ricus) and Saddled Wrasse (Notolabrus fucicola), the odacid Herring Cale (Odax cyanomelas), the serranid Barber Perch (Caesioperca rasor) and two scorpidid species, Sea Sweep (Scorpis aequipinnis) and Silver Sweep (Scorpis lineolata). Distributions and relative abundances (qualitative) are presented for 76 species at 26 sites in the region. The findings of this survey were supplemented with data from other surveys and sources to generate a checklist for fishes in the coastal waters of Wilsons Promontory and Comer Inlet. 23 I fishspecies of 92 families were identified to species level. An additional four species were only identified to higher taxonomic levels. These fishes were recorded from a range of habitat types, from freshwater streams to marine habitats (to 50 m deep).
    [Show full text]
  • Spatial and Temporal Variability in the Effects of Fish Predation on Macrofauna in Relation to Habitat Complexity and Cage Effects
    MARINE ECOLOGY PROGRESS SERIES Vol. 224: 231–250, 2001 Published December 19 Mar Ecol Prog Ser Spatial and temporal variability in the effects of fish predation on macrofauna in relation to habitat complexity and cage effects Jeremy S. Hindell1, 2,*, Gregory P. Jenkins3, Michael J. Keough1 1Department of Zoology, University of Melbourne, Parkville, Victoria 3010, Australia 2Queenscliff Marine Station, PO Box 138, Queenscliff, Victoria 3225, Australia 3Marine and Freshwater Research Institute, Weeroona Parade, Queenscliff, Victoria 3225, Australia ABSTRACT: The effects of predation by fishes, in relation to habitat complexity and periodicity of sampling, on abundances of fishes and macroinvertebrates were investigated using controlled caging experiments during summer 1999/2000 at multiple locations (Blairgowrie, Grand Scenic, and Kilgour) in Port Phillip Bay, Australia. A second experiment evaluated biological and physical cage effects. Sites and habitats, but not caging treatments, could generally be differentiated by the assem- blage structure of fishes. Regardless of species, small fishes were generally more abundant in seagrass than unvegetated sand, although the nature of this pattern was site- and time-specific. Depending on the site, abundances of fishes varied between cage treatments in ways that were con- sistent with neither cage nor predation effects (Grand Scenic), strong cage effects (Kilgour) or strong predation or cage effects (Blairgowrie). The abundance of syngnathids varied inconsistently between caging treatments and habitats within sites through time. Although they were generally more abun- dant in seagrass, whether or not predation or cage effects were observed depended strongly on the time of sampling. Atherinids and clupeids generally occurred more commonly over seagrass. In this habitat, atherinids varied between cage treatments in a manner consistent with strong cage effects, while clupeids varied amongst predator treatments in a way that could be explained either by cage or predation effects.
    [Show full text]
  • Biodiversity Summary: Port Phillip and Westernport, Victoria
    Biodiversity Summary for NRM Regions Species List What is the summary for and where does it come from? This list has been produced by the Department of Sustainability, Environment, Water, Population and Communities (SEWPC) for the Natural Resource Management Spatial Information System. The list was produced using the AustralianAustralian Natural Natural Heritage Heritage Assessment Assessment Tool Tool (ANHAT), which analyses data from a range of plant and animal surveys and collections from across Australia to automatically generate a report for each NRM region. Data sources (Appendix 2) include national and state herbaria, museums, state governments, CSIRO, Birds Australia and a range of surveys conducted by or for DEWHA. For each family of plant and animal covered by ANHAT (Appendix 1), this document gives the number of species in the country and how many of them are found in the region. It also identifies species listed as Vulnerable, Critically Endangered, Endangered or Conservation Dependent under the EPBC Act. A biodiversity summary for this region is also available. For more information please see: www.environment.gov.au/heritage/anhat/index.html Limitations • ANHAT currently contains information on the distribution of over 30,000 Australian taxa. This includes all mammals, birds, reptiles, frogs and fish, 137 families of vascular plants (over 15,000 species) and a range of invertebrate groups. Groups notnot yet yet covered covered in inANHAT ANHAT are notnot included included in in the the list. list. • The data used come from authoritative sources, but they are not perfect. All species names have been confirmed as valid species names, but it is not possible to confirm all species locations.
    [Show full text]
  • A Guide to the Management of Native Fish: Victorian Coastal Rivers and Wetlands 2007
    A guide to the management of native fish: Victorian Coastal Rivers and Wetlands 2007 A Guide to the Management of Native Fish: Victorian Coastal Rivers, Estuaries and Wetlands ACKNOWLEDGEMENTS This guide was prepared with the guidance and support of a Steering Committee, Scientific Advisory Group and an Independent Advisory Panel. Steering Committee – Nick McCristal (Chair- Corangamite CMA), Melody Jane (Glenelg Hopkins CMA), Kylie Bishop (Glenelg Hopkins CMA), Greg Peters (Corangamite CMA and subsequently Independent Consultant), Hannah Pexton (Melbourne Water), Rhys Coleman (Melbourne Water), Mark Smith (Port Phillip and Westernport CMA), Kylie Debono (West Gippsland CMA), Michelle Dickson (West Gippsland CMA), Sean Phillipson (East Gippsland CMA), Rex Candy (East Gippsland CMA), Pam Robinson (Australian Government NRM, Victorian Team), Karen Weaver (DPI Fisheries and subsequently DSE, Biodiversity and Ecosystem Services), Dr Jeremy Hindell (DPI Fisheries and subsequently DSE ARI), Dr Murray MacDonald (DPI Fisheries), Ben Bowman (DPI Fisheries) Paul Bennett (DSE Water Sector), Paulo Lay (DSE Water Sector) Bill O’Connor (DSE Biodiversity & Ecosystem Services), Sarina Loo (DSE Water Sector). Scientific Advisory Group – Dr John Koehn (DSE, ARI), Tarmo Raadik (DSE ARI), Dr Jeremy Hindell (DPI Fisheries and subsequently DSE ARI), Tom Ryan (Independent Consultant), and Stephen Saddlier (DSE ARI). Independent Advisory Panel – Jim Barrett (Murray-Darling Basin Commission Native Fish Strategy), Dr Terry Hillman (Independent Consultant), and Adrian Wells (Murray-Darling Basin Commission Native Fish Strategy-Community Stakeholder Taskforce). Guidance was also provided in a number of regional workshops attended by Native Fish Australia, VRFish, DSE, CMAs, Parks Victoria, EPA, Fishcare, Yarra River Keepers, DPI Fisheries, coastal boards, regional water authorities and councils.
    [Show full text]
  • Lipson Island Baseline Flora and Fauna Report and Assessment of Risk
    Donato Environmental Services ABN: 68083 254 015 Mobile: 0417 819 196 Int’l mobile: +61 417 819 196 Email: [email protected] Lipson Island baseline flora and fauna report and assessment of risk Final report to: Golder Associates November 2011 FINAL REPORT Lipson Island baseline flora and fauna report and assessment of risk Disclaimer This report has been prepared and produced by Donato Environmental Services (ABN 68083 254 015) in good faith and in line with the Terms of Engagement between Golder Associates Pty Ltd and Donato Environmental Services. Citation Madden-Hallett, D. M., Hammer, M., Gursansky, W. and Donato, D. B., 2011. Lipson Island baseline flora and fauna report and assessment of risk. For Golder Associates, Donato Environmental Services, Darwin. Table 1. Distribution Receivers Copies Date Issued Contact name Golder Associates Draft report (electronic) 11 July 2011 Rebecca Powlett DES Draft report (electronic) 31 August 2011 Danielle Madden- Hallett Golder Associates Final report (electronic) 16 September 2011Rebecca Powlett DES Electronic comment 26 October 2011 David Donato Golder Associates Final report (electronic) 30 October 2011 Jennifer Boniface DES Electronic comment 1 November 2011 David Donato Golder Associates Final report (electronic) 7 November 2011 Jennifer Boniface ii Lipson Island baseline flora and fauna report and assessment of risk Executive Golder Associates Pty Ltd approached Donato Environmental Services (DES) for a qualitative and quantitative assessment of flora and fauna within the Lipson summary Island Conservation Park, including the intertidal environments. Centrex Metals Ltd (Centrex) has extensive tenement holdings over iron ore resources and exploration targets on Eyre Peninsula in the southern Gawler Craton.
    [Show full text]
  • Ecological Assessment of the Potential Impacts on Merimbula Lake from Shallow Dunal Exfiltration of Effluent
    Bega Valley Shire Council FINAL REPORT 6 March 2013 Ecological Assessment of the Potential Impacts on Merimbula Lake from Shallow Dunal Exfiltration of Effluent Merimbula Effluent Management Options Investigation AECOM Merimbula Effluent Management Options Investigation Ecological Assessment of the Potential Impacts on Merimbula Lake from Shallow Dunal Exfiltration of Effluent Ecological Assessment of the Potential Impacts on Merimbula Lake from Shallow Dunal Exfiltration of Effluent Merimbula Effluent Management Options Investigation Prepared for Bega Valley Shire Council Prepared by AECOM Australia Pty Ltd Level 21, 420 George Street, Sydney NSW 2000, PO Box Q410, QVB Post Office NSW 1230, Australia T +61 2 8934 0000 F +61 2 8934 0001 www.aecom.com ABN 20 093 846 925 6 March 2013 60102089 AECOM in Australia and New Zealand is certified to the latest version of ISO9001 and ISO14001. © AECOM Australia Pty Ltd (AECOM). All rights reserved. AECOM has prepared this document for the sole use of the Client and for a specific purpose, each as expressly stated in the document. No other party should rely on this document without the prior written consent of AECOM. AECOM undertakes no duty, nor accepts any responsibility, to any third party who may rely upon or use this document. This document has been prepared based on the Client’s description of its requirements and AECOM’s experience, having regard to assumptions that AECOM can reasonably be expected to make in accordance with sound professional principles. AECOM may also have relied upon information provided by the Client and other third parties to prepare this document, some of which may not have been verified.
    [Show full text]
  • UNCOMMON, CRYPTIC and SITE-ASSOCIATED REEF FISHES: RESULTS of SURVEYS ALONG FLEURIEU PENINSULA & in ENCOUNTER BAY 2009
    UNCOMMON, CRYPTIC and SITE-ASSOCIATED REEF FISHES: RESULTS OF SURVEYS ALONG FLEURIEU PENINSULA & IN ENCOUNTER BAY 2009 J. Baker1, H. Crawford2, D. Muirhead3, S. Shepherd4, J. Brook5, A. Brown6, and C. Hall3 1 J.L. Baker, Marine Ecologist, Somerton Park, SA, 5044. Email: [email protected] 2 H. Crawford, Visual Artist [email protected] 3 Marine Life Society of South Australia (MLSSA) 4Senior Research Fellow, SARDI Aquatic Sciences PO Box 120 Henley Beach SA 5022 5 PO Box 111, Normanville, SA. 5204 6 Dept for Environment and Heritage, GPO Box 1047, Adelaide SA 5011 Photo: J. Baker Report for: Adelaide and Mt Lofty Ranges Natural Resources Management Board August 2009 UNCOMMON, CRYPTIC and SITE-ASSOCIATED REEF FISHES: RESULTS OF SURVEYS ALONG FLEURIEU PENINSULA & IN ENCOUNTER BAY 2009 SUMMARY Reef locations along the Fleurieu Peninsula and Encounter Bay were surveyed by diving and snorkelling, from December 2008 to June 2009. The surveys are part of a series we began in 2007, through which we have aimed to (i) develop a suitable non-destructive technique to search for various uncommon reef fishes (mostly benthic, and many cryptic) throughout South Australia; and (ii) record and photograph such fishes, in order to learn more about their distribution, habitats, and habits. Our target list comprises more than 50 species from 14 families, for which little information is available on full distribution within South Australia, and habitat. Examples of our records during the 2009 survey period included (i) one uncommonly recorded endemic
    [Show full text]
  • 2020 Great Victorian Fish Count
    EXPLORING OUR HOME TURF 2020 GREAT VICTORIAN FISH COUNT SHANDY MAE YAP NICOLE MERTENS KADE MILLS Victorian National Parks Association Our vision is to ensure Victoria is a place with a diverse and healthy natural environment that is protected, respected and enjoyed by all. We work with all levels of government, the scientific community and the general community to achieve long term, best practice environmental outcomes and help shape the agenda for creating and managing national parks, conservation reserves and other important natural areas across land and sea in Victoria. We are also Victoria’s largest bushwalking club and provide a range of education, citizen science and activity programs that encourage Victorians to get active for nature. ReefWatch ReefWatch is the Victorian National Parks Association’s marine citizen science program. It provides projects that engage divers, snorkelers, rock pool ramblers and beach combers to contribute their observations, images and knowledge to expand our understanding of Victoria’s unique marine life. ReefWatch coordinates a number of marine citizen science programs, including the Melbourne Sea Slug Census, Dragon Quest and the Great Victorian Fish Count. Acknowledgements Parks Victoria: Mark Rodrigue, Dani Rizzo, Peter Hay, Jill Wheeler, Thierry Rolland Coastcare Victoria: Phillip Wierzbowski Museums Victoria and Redmap Victoria: Dianne Bray Atlas of Living Australia: Peter Brenton Participating groups: Australian Dive Instruction, Bass Strait Aquatic Club, Daktari Surf/Bike/Dive, Dive and Dive,
    [Show full text]
  • Appendix I Sustainable Project Management (2018) Marine Impact Assessment
    Yumbah Nyamat Works Approval Application October 2018 Appendix I Sustainable Project Management (2018) Marine Impact Assessment Table of contents 1. Introduction ............................................................................................................................................... 1 1.1 Purpose of this report .......................................................................................................... 1 2. Methodology ............................................................................................................................................. 2 2.1 Marine habitat assessment ................................................................................................. 2 3. The Marine Environment .......................................................................................................................... 3 3.1 General Characteristics ........................................................................................................ 3 3.2 EPBC Act Protected Matters ................................................................................................ 3 3.4 Victorian Biodiversity Atlas .................................................................................................. 5 3.5 Marine Benthic Survey ........................................................................................................ 5 4. Marine Impact Assessment .....................................................................................................................
    [Show full text]
  • Exploitation and Trade of Australian Seahorses, Pipehorses, Sea Dragons and Pipefishes (Family Syngnathidae)
    Oryx Vol 40 No 2 April 2006 Exploitation and trade of Australian seahorses, pipehorses, sea dragons and pipefishes (Family Syngnathidae) Keith M. Martin-Smith and Amanda C.J. Vincent Abstract Seahorses and their syngnathid relatives have both volume and value. Research is urgently needed provided a focus for efforts to ensure sustainable use of to evaluate the impacts and sustainability of trawling marine resources, with new international trade controls on pipehorse populations. Australia is also the sole (CITES Appendix II) implemented in May 2004. We dem- supplier of two sea dragon species, Phycodurus eques onstrate how a study of international trade can be used to and Phyllopteryx taeniolatus, for the live aquarium trade. assess relative levels of threat and set domestic research Although lucrative, the number of wild-caught indi- and conservation priorities. Australia has remarkably viduals involved in this trade was relatively low and high syngnathid biodiversity with at least 14 seahorse probably of low conservation risk relative to habitat species, two endemic sea dragon species, and 90 species loss. Exports of seahorses and other pipefish species, and of pipefishes and pipehorses found in its territorial imports of all syngnathid species, are minor on a global waters. Our objectives were to quantify species, trade scale, although the burgeoning aquaculture industry for routes, volumes, values and temporal trends in syngna- seahorses requires careful evaluation for its potential thid trade to and from Australia. We found that Australia impacts on wild populations. is probably the major global supplier of dried pipehorses Solegnathus spp.. These fishes, including at least one Keywords Aquaculture, aquarium, bycatch, exports, endemic species, are sourced from trawl bycatch and imports, pipefish, pipehorse, sea dragon, Syngnathidae, comprise Australia’s largest syngnathid export, by traditional medicine.
    [Show full text]
  • The Etyfish Project © Christopher Scharpf and Kenneth J
    SYNGNATHIFORMES (part 1) · 1 The ETYFish Project © Christopher Scharpf and Kenneth J. Lazara COMMENTS: v. 5.0 - 10 Jan. 2021 Series SYNGNATHARIA Order SYNGNATHIFORMES (part 1 of 2) Suborder SYNGNATHOIDEI Family AULOSTOMIDAE Trumpetfishes Aulostomus Lacepède 1803 aulon, tube; stomus, mouth, referring to small mouth at end of long, compressed tube Aulostomus chinensis (Linnaeus 1766) -ensis, suffix denoting place: China, originally based on more than one species described from multiple sources, including “Acus chinensis maxima, corpore compresso” of China from Petiver (1702) Aulostomus maculatus Valenciennes 1841 spotted, referring to black or dark-brown round spots, often concentrated on back and belly but sometimes extending sparsely to the sides Aulostomus strigosus Wheeler 1955 slender, allusion not explained, but like its congeners it is a slender (elongate and compressed) fish Family CENTRISCIDAE Shrimpfishes and Snipefishes 5 genera · 13 species Subfamily Centriscinae Shrimpfishes Aeoliscus Jordan & Starks 1902 “moving,” according to the authors, allusion not explained but certainly referring to movable dorsal-fin spine, compared to fixed or rigid dorsal-fin spine of Centriscus Aeoliscus punctulatus (Bianconi 1854) diminutive of punctum, spot, referring to scattering of small black spots on body Aeoliscus strigatus (Günther 1861) striped, referring to black streak running from snout, through eye and base of pectoral fin, and along lower edge of dorsal cuirass Centriscus Linnaeus 1758 diminutive of kentron, thorn or spine, presumably
    [Show full text]
  • Exploitation and Trade of Australian Seahorses, Pipehorses, Sea Dragons and Pipefishes (Family Syngnathidae)
    Oryx Vol 40 No 2 April 2006 Exploitation and trade of Australian seahorses, pipehorses, sea dragons and pipefishes (Family Syngnathidae) Keith M. Martin-Smith and Amanda C.J. Vincent Abstract Seahorses and their syngnathid relatives have both volume and value. Research is urgently needed provided a focus for efforts to ensure sustainable use of to evaluate the impacts and sustainability of trawling marine resources, with new international trade controls on pipehorse populations. Australia is also the sole (CITES Appendix II) implemented in May 2004. We dem- supplier of two sea dragon species, Phycodurus eques onstrate how a study of international trade can be used to and Phyllopteryx taeniolatus, for the live aquarium trade. assess relative levels of threat and set domestic research Although lucrative, the number of wild-caught indi- and conservation priorities. Australia has remarkably viduals involved in this trade was relatively low and high syngnathid biodiversity with at least 14 seahorse probably of low conservation risk relative to habitat species, two endemic sea dragon species, and 90 species loss. Exports of seahorses and other pipefish species, and of pipefishes and pipehorses found in its territorial imports of all syngnathid species, are minor on a global waters. Our objectives were to quantify species, trade scale, although the burgeoning aquaculture industry for routes, volumes, values and temporal trends in syngna- seahorses requires careful evaluation for its potential thid trade to and from Australia. We found that Australia impacts on wild populations. is probably the major global supplier of dried pipehorses Solegnathus spp.. These fishes, including at least one Keywords Aquaculture, aquarium, bycatch, exports, endemic species, are sourced from trawl bycatch and imports, pipefish, pipehorse, sea dragon, Syngnathidae, comprise Australia’s largest syngnathid export, by traditional medicine.
    [Show full text]