SAFS Report 2018
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Assessing the Effectiveness of Surrogates for Conserving Biodiversity in the Port Stephens-Great Lakes Marine Park
Assessing the effectiveness of surrogates for conserving biodiversity in the Port Stephens-Great Lakes Marine Park Vanessa Owen B Env Sc, B Sc (Hons) School of the Environment University of Technology Sydney Submitted in fulfilment for the requirements of the degree of Doctor of Philosophy September 2015 Certificate of Original Authorship I certify that the work in this thesis has not been previously submitted for a degree nor has it been submitted as part of requirements for a degree except as fully acknowledged within the text. I also certify that the thesis has been written by me. Any help that I have received in my research work and preparation of the thesis itself has been acknowledged. In addition, I certify that all information sources and literature used as indicated in the thesis. Signature of Student: Date: Page ii Acknowledgements I thank my supervisor William Gladstone for invaluable support, advice, technical reviews, patience and understanding. I thank my family for their encouragement and support, particularly my mum who is a wonderful role model. I hope that my children too are inspired to dream big and work hard. This study was conducted with the support of the University of Newcastle, the University of Technology Sydney, University of Sydney, NSW Office of the Environment and Heritage (formerly Department of Environment Climate Change and Water), Marine Park Authority NSW, NSW Department of Primary Industries (Fisheries) and the Integrated Marine Observing System (IMOS) program funded through the Department of Industry, Climate Change, Science, Education, Research and Tertiary Education. The sessile benthic assemblage fieldwork was led by Dr Oscar Pizarro and undertaken by the University of Sydney’s Australian Centre for Field Robotics. -
Comparisons Between the Biology of Two Species of Whiting (Sillaginidiae) in Shark Bay, Western Australia
Comparisons between the biology of two species of whiting (Sillaginidiae) in Shark Bay, Western Australia By Peter Coulson Submitted for the Honours Degree of Murdoch University August 2003 1 Abstract Golden-lined whiting Sillago analis and yellow-fin whiting Sillago schomburgkii were collected from waters within Shark Bay, which is located at ca 26ºS on the west coast of Australia. The number of circuli on the scales of S. analis was often less than the number of opaque zones in sectioned otoliths of the same fish. Furthermore, the number of annuli visible in whole otoliths of S. analis was often less than were detectable in those otoliths after sectioning. The magnitude of the discrepancies increased as the number of opaque zones increased. Consequently, the otoliths of S. analis were sectioned in order to obtain reliable estimates of age. The mean monthly marginal increments on sectioned otoliths of S. analis and S. schomburgkii underwent a pronounced decline in late spring/early summer and then rose progressively during summer and autumn. Since these trends demonstrated that opaque zones are laid down annually in the otoliths of S. analis and S. schomburgkii from Shark Bay, their numbers could be used to help age this species in this marine embayment. The von Bertalanffy growth parameters, L∞, k and to derived from the total lengths at age for individuals of S. analis , were 277 mm, 0.73 year -1 and 0.02 years, respectively, for females and 253 mm, 0.76 year -1 and 0.10 years, respectively. Females were estimated to attain lengths of 141, 211, 245 and 269 mm after 1, 2, 3 and 5 years, compared with 124, 192, 224 and 247 mm for males at the corresponding ages. -
Information Sheet
Illustration © R. Swainston/anima.net.au Information sheet Yellowfin whiting (Sillago schombergkii) Distribution Identification Yellowfin whiting (also known as western sand Adults have no distinguishing body markings and are whiting) are endemic to south-western Australia from best identified by their yellow ventral and anal fins Western Australia (Onslow) to South Australia (Gulf St and a weakly forked tail. Juveniles have faint black Vincent). WA and SA host separate breeding stocks. blotches on the body and may be confused with juvenile western trumpeter whiting. Stock structure and movement In WA, populations within the Gascoyne Coast Growth Bioregion and West Coast Bioregion are believed Can reach a maximum of 427 mm total length (TL) to have limited connectivity and so are regarded as and 12 years of age. Females and males attain separate stocks. sexual maturity at 2 years, at 200 and 190 mm TL, respectively. Females grow slightly larger than males. In the West Coast Bioregion, some fish live in estuaries for much the year, but these fish migrate Reproduction to sea to join their ocean-dwelling counterparts to Spawning typically occurs at water temperatures spawn in late spring/early summer. Hence, fish of 22-24 ºC. Spawning occurs August-December across the West Coast Bioregion belong to the same in northern areas (e.g. Shark Bay) and December- breeding stock (e.g. fish caught in the Peel-Harvey February in southern areas (e.g. Perth). Spawning Estuary are part of the same population as those in occurs over a longer period in northern areas Geographe Bay or Jurien Bay). -
Catalogue of Protozoan Parasites Recorded in Australia Peter J. O
1 CATALOGUE OF PROTOZOAN PARASITES RECORDED IN AUSTRALIA PETER J. O’DONOGHUE & ROBERT D. ADLARD O’Donoghue, P.J. & Adlard, R.D. 2000 02 29: Catalogue of protozoan parasites recorded in Australia. Memoirs of the Queensland Museum 45(1):1-164. Brisbane. ISSN 0079-8835. Published reports of protozoan species from Australian animals have been compiled into a host- parasite checklist, a parasite-host checklist and a cross-referenced bibliography. Protozoa listed include parasites, commensals and symbionts but free-living species have been excluded. Over 590 protozoan species are listed including amoebae, flagellates, ciliates and ‘sporozoa’ (the latter comprising apicomplexans, microsporans, myxozoans, haplosporidians and paramyxeans). Organisms are recorded in association with some 520 hosts including mammals, marsupials, birds, reptiles, amphibians, fish and invertebrates. Information has been abstracted from over 1,270 scientific publications predating 1999 and all records include taxonomic authorities, synonyms, common names, sites of infection within hosts and geographic locations. Protozoa, parasite checklist, host checklist, bibliography, Australia. Peter J. O’Donoghue, Department of Microbiology and Parasitology, The University of Queensland, St Lucia 4072, Australia; Robert D. Adlard, Protozoa Section, Queensland Museum, PO Box 3300, South Brisbane 4101, Australia; 31 January 2000. CONTENTS the literature for reports relevant to contemporary studies. Such problems could be avoided if all previous HOST-PARASITE CHECKLIST 5 records were consolidated into a single database. Most Mammals 5 researchers currently avail themselves of various Reptiles 21 electronic database and abstracting services but none Amphibians 26 include literature published earlier than 1985 and not all Birds 34 journal titles are covered in their databases. Fish 44 Invertebrates 54 Several catalogues of parasites in Australian PARASITE-HOST CHECKLIST 63 hosts have previously been published. -
New Distributional Record of the Endemic Estuarine Sand Whiting, Sillago Vincenti Mckay, 1980 from the Pichavaram Mangrove Ecosystem, Southeast Coast of India
Indian Journal of Geo Marine Sciences Vol. 47 (03), March 2018, pp. 660-664 New distributional record of the endemic estuarine sand whiting, Sillago vincenti McKay, 1980 from the Pichavaram mangrove ecosystem, southeast coast of India Mahesh. R1δ, Murugan. A2, Saravanakumar. A1*, Feroz Khan. K1 & Shanker. S1 1CAS in Marine Biology, Faculty of Marine Sciences, Annamalai University, Porto Novo, Tamil Nadu, India - 608 502. 2Department of Value Added Aquaculture (B.Voc.), Vivekananda College, Agasteeswaram, India - 629 701. δ Present Address: National Centre for Sustainable Coastal Management, MoEF & CC, Chennai, India - 600 025. *[E-mail: [email protected]] Received 27 December 2013 ; revised 17 November 2016 The Sillaginids, commonly known as sand whiting are one among the common fishes caught by the traditional fishers in estuarine ecosystems all along the Tamil Nadu coast. The present study records the new distributional range extension for Sillago vincenti from the waters of Pichavaram mangrove, whereas earlier reports were restricted to only the Palk Bay and Gulf of Mannar regions of the Tamil Nadu coast, whereas it enjoys a wide range of distribution both in the east and west coast of India. This study marks the additional extension of the distributional record for S. vincenti in the east coast of India. Biological information on these fishes will have ecological applications particularly on account on their extreme abundance in the mangrove waters. The present study is based on the collection of specimens from handline fishing practices undertaken in the shallow waters of Pichavaram mangroves, on the southeast coast of India. [Keywords: Sillagnids, Sillago vincenti, Pichavaram, India] Introduction Sillaginopodys and Sillaginops)8. -
Seafood Product Names List
SEAFOOD PRODUCT NAMES LIST QTY PRODUCT NAME SCR # SCR # TICKET TICKET ** FRESH SALMON ROE (CAVIER) - [ check spelling on cavier] 814A 1 KG PACKET EXTENDER 234A 1/2 DOZEN EXTRA LARGE SYDNEY ROCK OYSTERS 714A 1/2 DOZEN LARGE SYDNEY ROCK OYSTERS 714A 1/2 DOZEN UNOPENED PACIFIC OYSTERS 714A 1/2 DOZEN UNOPENED SYDNEY ROCK OYSTERS 715A 2 DOZEN OYSTERS 769A 3 DOZ UNOPENED OYSTERS 330A AFRICAN CARP 977 ALBACORE (TUNA) STEAKS 981 ALBACORE FILLETS 404A ALBACORE STEAKS 665A ALBACORE TUNA CUTLETS 1037 1006 ALBACORE TUNA STEAKS 416A FT7L FT8L ALFONSINA FILLETS 254A ALFONSINO FILLETS 694A ALFONSINO RED PERCH 870A ALMOND TROUT 456A FT7L FT8L ALMOST BARRAMUNDI 229A AMBERJACK FILLETS 436A FT7L FT8L ANCHOVIES 665A ANGEL FISH FILLETS 506A 507A FT7L FT8L ANGEL SHARK 565A FT7L FT8L ANTONIOS HOME MADE DIPPING SAUCES 773A AQUATAS A GRADE Cold Smoked Atlantic Salmon 520A Aquatas Cold Smoked Atalantic Salmon Cockt Pces 520A FT7L FT8L AQUATAS COLD SMOKED ATLANTIC SLAMON 520A FT7L FT8L AQUATAS COLD SMOKED OCEAN TROUT 520A FT7L FT8L AQUATAS OAK SMOKED Pastrami Atlantic Salmon 520A FT7L FT8L AQUATAS PREMIUM Cold Smoked Atlantic Salmon 520A FT7L FT8L AQUATAS Premium Cold Smoked Ocean Trout 520A FT7L FT8L AQUATAS SMOKED SALMON 588A FT7L FT8L AQUATAS SMOKED SALMON PIECES 737A AQUATAS TASMANIAN Smoked Salmon (Gravalax) 520A ARROW SQUID 543A 300A FT7L FT8L ARROW SQUID CALAMARI 701A ATLANTIC SALMON 416A 29A FT7L FT8L ATLANTIC SALMON (APPROX. (170-200g) 434A FT7L FT8L ATLANTIC SALMON (SASHIMI) 681A ATLANTIC SALMON BELLY 842A ATLANTIC SALMON CAVIAR JAR 891A ATLANTIC SALMON -
Fishing and fisheries of Moreton
https://moretonbayfoundation.org/ 1 Moreton Bay Quandamooka & Catchment: Past, present, and future Chapter 7 Industry Protected: Fishing and fisheries of Moreton Bay Abstract Moreton Bay is one of the most intensely used coastal systems in Australia and supports some of Queensland’s most productive fisheries, including Indigenous, commercial, recreational and charter sectors. This paper explores the economic and cultural value of these fisheries to the Moreton Bay region and the challenges they face. Fishing is recognised as one of Queensland’s oldest industries. Marine resources were harvested by Indigenous peoples long before European settlement and continue to form an important part of Indigenous culture today. Commercial fisheries operating within Moreton Bay are valued at $24m per annum, and target a variety of species groups including prawns, crabs, squid and finfish such as mullet, bream and whiting. Direct expenditure by the recreational sector in Moreton Bay is estimated to be ~$194m per annum, with fishers harvesting mud crabs, sand whiting, snapper, tailor and bream, among others. Despite the longevity of these sectors, a number of challenges exist. These include managing risks related to climate change, a growing urban population, and the need to mitigate environmental impacts from fishing and other marine activities. Interactions with other management sectors, including marine park planning and native title rights, will also need to evolve if we are to ensure a sustainable future for the fisheries of Moreton Bay. Keywords: charter fishing, indigenous fishing, industry, prawn, recreational fishing, trawl Introduction Moreton Bay is one of the most intensively fished regions in Queensland. Although it comprises just 3% of the Queensland coastline, it produces about 12% of Queensland’s fish catch ([i]) and supports some of the state’s most productive commercial and recreational fisheries ([ii]). -
Report N9 37
REPORTN9 37 Plblishod by the Dir€.ior ol tish€ri€5 and Wildllla, Porth, under the autho.ity ol the H.n. Minister for rish€ries and Wildlitc An Inventoryof the MarineResources of the BunburyMarine Area and GeographeBay BY MICHAELH. WALKER 1979 6L6I -IfVHSIW U3)"IVM 'H .f,q IVglHdvugolg 0NVVIUV llllUvl^l IUnSNn[]Hl l0 silutl0silINIUVI/'JlHl l0 IU0INSAIIjI IUOd]U j H,tusiI , ecer.re,tr,epTeTepv g oT eJTTpTTM pue seT.reqs;g 3:o 4uaur4.redaq tIZ!90 CONTENTS ABSTMCT 5 I I NTRODUCTION 6 II THEMARIt'|E RESOURCE ASCAPTURED BYCONVENTIONAL FISHINGIVIETHODS 6 I. INTRODUCTION 6 2. METHODS 3. THE RESOURCECAPTURED BY 9 A. SET LINING 9 B. TRAPPING L2 C. SET NETTING L2 D. EAND LINING 13 E. TROLLING t-3 F. BEACH SEINING 14 G. RING NETTING L4 H. TRAWT-,ING t_f, r. LIGHT ATTRACTION AT NIGIIT I6 III ANINVENTORY OFTHE FISH RESOURCE I7 T. INTRODUCTION L7 2. SUI"IMARYoF SoMEAsPEcTs oF THEBIoLoGY oF GEoGRAPHEsly/sut'tsuRy MARINE FIsHEs 18 3. cHEcKLIsroF FISHESoF THE eeoenepHegny/ BUNBURYMRINE AREAWITH COMMENTS ON THEIRECOLOGICAL STATUS t9 IV SUIvlIvlARYANDCONCLUSIONS 2L V ACKNOI^|LTDGEIIENTS 23 VI REFERENCES 23 ' 9t ITEIUVtrNrtrvn rUngNng ,/IVS Sg'Tgu9OS9 SIT.IJNIII'IIII4 SVSTTE9NIT'IWVS .T 3Un9H 'vgnE 6€ sNIutn rungNos sg.r qNv tvg eHdw9ose .{o ssHsrJl sHJ ,40 ,rsITxcsHJ '8 '916T !L UStilEAON qNv rrEdv 'sz6T usw{sAoN,/ussorcoNr sssrnuo TSAENS S$UE,I ONIUNC qSUO,IiTYC SEHSIJ IiIOU.II qg,rJsTToc NoI,rvt[tIo.rNI T\rJreoToTg ,ilo .f,unnnns '^ LL I SHaVE9oS9 NIH.IIM SNOI&Vf,O{I UO.!I SSgfiVJ SNISS ESVES '9 TT 'ssgSr\fJ ilsN HsrJ vgrw sNruw{ ruflsNns/rvs sgdvEgosrg 's A7 . -
Biodiversity Summary: Cape York, Queensland
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. -
Stock Assessments of Bream, Whiting and Flathead (Acanthopagrus Australis, Sillago Ciliata and Platycephalus Fuscus) in South East Queensland
Department of Agriculture and Fisheries Stock assessments of bream, whiting and flathead (Acanthopagrus australis, Sillago ciliata and Platycephalus fuscus) in South East Queensland April 2019 This publication has been compiled by George M. Leigh1, Wen-Hsi Yang2, Michael F. O’Neill3, Jason G. McGilvray4 and Joanne Wortmann3 for the Department of Agriculture and Fisheries. It provides assessments of the status of south east Queensland’s populations of yellowfin bream, sand whiting and dusky flathead, three of Australia’s most commonly fished species. 1Agri-Science Queensland, Floor 5, 41 George Street, Brisbane, Queensland 4000, Australia 2Centre for Applications in Natural Resource Mathematics (CARM), School of Mathematics and Physics, The University of Queensland, St Lucia, Queensland 4072, Australia 3Agri-Science Queensland, Maroochy Research Facility, 47 Mayers Road, Nambour, Queensland 4560, Australia 4Fisheries Queensland, Department of Agriculture and Fisheries, Level 1A East, Ecosciences Precinct, 41 Boggo Rd, Dutton Park, Queensland 4102, Australia © The State of Queensland, 2019 Cover photos: Yellowfin bream Acanthopagrus australis, sand whiting Sillago ciliata and dusky flathead Platycephalus fuscus (source: John Turnbull, Creative Commons by Attribution, Non-commercial, Share-alike licence). The Queensland Government supports and encourages the dissemination and exchange of its information. The copyright in this publication is licensed under a Creative Commons by Attribution 4.0 International (CC BY 4.0) licence. Under this licence you are free, without having to seek our permission, to use this publication in accordance with the licence terms. You must keep intact the copyright notice and attribute the State of Queensland as the source of the publication. Note: Some content in this publication may have different licence terms as indicated. -
Description of Key Species Groups in the East Marine Region
Australian Museum Description of Key Species Groups in the East Marine Region Final Report – September 2007 1 Table of Contents Acronyms........................................................................................................................................ 3 List of Images ................................................................................................................................. 4 Acknowledgements ....................................................................................................................... 5 1 Introduction............................................................................................................................ 6 2 Corals (Scleractinia)............................................................................................................ 12 3 Crustacea ............................................................................................................................. 24 4 Demersal Teleost Fish ........................................................................................................ 54 5 Echinodermata..................................................................................................................... 66 6 Marine Snakes ..................................................................................................................... 80 7 Marine Turtles...................................................................................................................... 95 8 Molluscs ............................................................................................................................ -
Population Parameters of Indian Sand Whiting Sillago Sihama (Forsskal) from Estuaries of Southern Karnataka
J. mar. biol. Ass. India, 2003, 45 (1) : 54 - 60 Population parameters of Indian sand whiting Sillago sihama (Forsskal) from estuaries of southern Karnataka. K.S. Udupa, C.H. Raghavendra, Vinayak Bevinahalli, G. R. Aswatha Reddy and M. Averel College of Fisheries, Kankanady, Mangalore - 575 002, India Abstract The Indian sand whiting, Sillago sihama, occurring in the estuaries of Karnataka along the southwest coast of India was found to attain a mean length of 17.1,25.2,29.2 and 31.1 cm at the end of 1-4 years respectively. From the length-converted catch curve, the total fishing mor- tality Z was estimated as 3.79 year-' whereas from Jones and van Zalinge method Z was esti- mated to be 3.28. The natural mortality M was estimated to be 1.41 which gave F = 2.38. The exploitation rate E = 0.63 gave an indication that S. sihama fishery is facing moderately higher fishing pressure in these estuaries. lc was estimated as 14.45 cm, Im=16.5cm and lopt=20.7cm. The length-weight'relationship was found to be W = 0.02471 L 2.56. Wmwas estimated as 197g. The life span of the species is around 4.22 years. A note on the spawning season and recruit- ment pattern is also included in this paper. Introduction some of them are commercially important. Even though many studies have been An attempt is made in this paper to esti- conducted on the stock assessment of mate the population parameters and to marine fishes from India, very few attempts study the spawning season of Indian sand have been made on the stock assessment whiting S.