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Bycatch</title> <meta name="description" content="Search results for: Bycatch"> <meta name="keywords" content="Bycatch"> <meta name="viewport" content="width=device-width, initial-scale=1, minimum-scale=1, maximum-scale=1, user-scalable=no"> <meta charset="utf-8"> <link href="https://cdn.waset.org/favicon.ico" type="image/x-icon" rel="shortcut icon"> <link href="https://cdn.waset.org/static/plugins/bootstrap-4.2.1/css/bootstrap.min.css" rel="stylesheet"> <link href="https://cdn.waset.org/static/plugins/fontawesome/css/all.min.css" rel="stylesheet"> <link href="https://cdn.waset.org/static/css/site.css?v=150220211555" rel="stylesheet"> </head> <body> <header> <div class="container"> <nav class="navbar navbar-expand-lg navbar-light"> <a class="navbar-brand" href="https://waset.org"> <img src="https://cdn.waset.org/static/images/wasetc.png" alt="Open Science Research Excellence" title="Open Science Research Excellence" /> </a> <button class="d-block d-lg-none navbar-toggler ml-auto" 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class="input-group"> <i class="fas fa-search"></i> <input type="text" class="search-query" name="q" placeholder="Author, Title, Abstract, Keywords" value="Bycatch"> <input type="submit" class="btn_search" value="Search"> </div> </div> </form> </div> </div> <div class="row mt-3"> <div class="col-sm-3"> <div class="card"> <div class="card-body"><strong>Commenced</strong> in January 2007</div> </div> </div> <div class="col-sm-3"> <div class="card"> <div class="card-body"><strong>Frequency:</strong> Monthly</div> </div> </div> <div class="col-sm-3"> <div class="card"> <div class="card-body"><strong>Edition:</strong> International</div> </div> </div> <div class="col-sm-3"> <div class="card"> <div class="card-body"><strong>Paper Count:</strong> 6</div> </div> </div> </div> <h1 class="mt-3 mb-3 text-center" style="font-size:1.6rem;">Search results for: Bycatch</h1> <div class="card paper-listing mb-3 mt-3"> <h5 class="card-header" style="font-size:.9rem"><span class="badge badge-info">6</span> Diving Behaviour of White-Chinned Petrels and Its Relevance for Mitigating Longline Bycatch</h5> <div class="card-body"> <p class="card-text"><strong>Authors:</strong> <a href="https://publications.waset.org/abstracts/search?q=D.%20P.%20Rollinson">D. P. Rollinson</a>, <a href="https://publications.waset.org/abstracts/search?q=B.%20J.%20Dilley"> B. J. Dilley</a>, <a href="https://publications.waset.org/abstracts/search?q=P.%20G.%20Ryan"> P. G. Ryan</a> </p> <p class="card-text"><strong>Abstract:</strong></p> The white-chinned petrel (Procellaria aequinoctialis) is the seabird species most commonly killed by Southern Hemisphere longline fisheries. Despite the importance of diving ability for mitigating longline bycatch, little is known of this species’ diving behaviour. We obtained data from temperature–depth recorders from nine white-chinned petrels breeding on Marion Island, southwestern Indian Ocean, during the late incubation and chickrearing period. Maximum dive depth (16 m) was slightly deeper than the previous estimate (13 m), but varied considerably among individuals (range 2–16 m). Males dived deeper than females, and birds feeding chicks dived deeper than incubating birds, but dive rate did not differ between the sexes. Time of day had no significant effect on dive depth or rate. Our findings will help to improve the design and performance of mitigation measures aimed at reducing seabird bycatch in longline fisheries, such as the calculation of minimum line sink rates and optimum aerial coverage of bird-scaring lines. <p class="card-text"><strong>Keywords:</strong> <a href="https://publications.waset.org/abstracts/search?q=dive%20depth" title="dive depth">dive depth</a>, <a href="https://publications.waset.org/abstracts/search?q=dive%20duration" title=" dive duration"> dive duration</a>, <a href="https://publications.waset.org/abstracts/search?q=temperature%E2%80%93depth%20recorders" title=" temperature–depth recorders"> temperature–depth recorders</a>, <a href="https://publications.waset.org/abstracts/search?q=seabirds" title=" seabirds"> seabirds</a>, <a href="https://publications.waset.org/abstracts/search?q=bird-scaring%20lines" title=" bird-scaring lines"> bird-scaring lines</a> </p> <a href="https://publications.waset.org/abstracts/15502/diving-behaviour-of-white-chinned-petrels-and-its-relevance-for-mitigating-longline-bycatch" class="btn btn-primary btn-sm">Procedia</a> <a href="https://publications.waset.org/abstracts/15502.pdf" target="_blank" class="btn btn-primary btn-sm">PDF</a> <span class="bg-info text-light px-1 py-1 float-right rounded"> Downloads <span class="badge badge-light">573</span> </span> </div> </div> <div class="card paper-listing mb-3 mt-3"> <h5 class="card-header" style="font-size:.9rem"><span class="badge badge-info">5</span> A Study on Aquatic Bycatch Mortality Estimation Due to Prawn Seed Collection and Alteration of Collection Method through Sustainable Practices in Selected Areas of Sundarban Biosphere Reserve (SBR), India</h5> <div class="card-body"> <p class="card-text"><strong>Authors:</strong> <a href="https://publications.waset.org/abstracts/search?q=Samrat%20Paul">Samrat Paul</a>, <a href="https://publications.waset.org/abstracts/search?q=Satyajit%20Pahari"> Satyajit Pahari</a>, <a href="https://publications.waset.org/abstracts/search?q=Krishnendu%20Basak"> Krishnendu Basak</a>, <a href="https://publications.waset.org/abstracts/search?q=Amitava%20Roy"> Amitava Roy</a> </p> <p class="card-text"><strong>Abstract:</strong></p> Fishing is one of the pivotal livelihood activities, especially in developing countries. Today it is considered an important occupation for human society from the era of human settlement began. In simple terms, non-target catches of any species during fishing can be considered as ‘bycatch,’ and fishing bycatch is neither a new fishery management issue nor a new problem. Sundarban is one of the world’s largest mangrove land expanding up to 10,200 sq. km in India and Bangladesh. This largest mangrove biome resource is used by the local inhabitants commercially to run their livelihood, especially by forest fringe villagers (FFVs). In Sundarban, over-fishing, especially post larvae collection of wild Penaeus monodon, is one of the major concerns, as during the collection of P. monodon, different aquatic species are destroyed as a result of bycatch mortality which changes in productivity and may negatively impact entire biodiversity, of the ecosystem. Wild prawn seed collection gear like a small mesh sized net poses a serious threat to aquatic stocks, where the collection isn’t only limited to prawn seed larvae. As prawn seed collection processes are inexpensive, require less monetary investment, and are lucrative; people are easily engaged here as their source of income. Wildlife Trust of India’s (WTI) intervention in selected forest fringe villages of Sundarban Tiger Reserve (STR) was to estimate and reduce the mortality of aquatic bycatches by involving local communities in newly developed release method and their time engagement in prawn seed collection (PSC) by involving them in Alternate Income Generation (AIG). The study was conducted for their taxonomic identification during the period of March to October 2019. Collected samples were preserved in 70% ethyl alcohol for identification, and all the preserved bycatch samples were identified morphologically by the expertise of the Zoological Survey of India (ZSI), Kolkata. Around 74 different aquatic species, where 11 different species are molluscs, 41 fish species, out of which 31 species were identified, and 22 species of crustacean collected, out of which 18 species were identified. Around 13 different species belong to a different order, and families were unable to identify them morphologically as they were collected in the juvenile stage. The study reveals that for collecting one single prawn seed, eight individual life of associated faunas are being lost. Zero bycatch mortality is not practical; rather, collectors should focus on bycatch reduction by avoiding capturing, allowing escaping, and mortality reduction, and must make changes in their fishing method by increasing net mesh size, which will avoid non-target captures. But as the prawns are small in size (generally 1-1.5 inches in length), thus increase net size making economically less or no profit for collectors if they do so. In this case, returning bycatches is considered one of the best ways to a reduction in bycatch mortality which is a more sustainable practice. <p class="card-text"><strong>Keywords:</strong> <a href="https://publications.waset.org/abstracts/search?q=bycatch%20mortality" title="bycatch mortality">bycatch mortality</a>, <a href="https://publications.waset.org/abstracts/search?q=biodiversity" title=" biodiversity"> biodiversity</a>, <a href="https://publications.waset.org/abstracts/search?q=mangrove%20biome%20resource" title=" mangrove biome resource"> mangrove biome resource</a>, <a href="https://publications.waset.org/abstracts/search?q=sustainable%20practice" title=" sustainable practice"> sustainable practice</a>, <a href="https://publications.waset.org/abstracts/search?q=Alternate%20Income%20Generation%20%28AIG%29" title=" Alternate Income Generation (AIG)"> Alternate Income Generation (AIG)</a> </p> <a href="https://publications.waset.org/abstracts/164722/a-study-on-aquatic-bycatch-mortality-estimation-due-to-prawn-seed-collection-and-alteration-of-collection-method-through-sustainable-practices-in-selected-areas-of-sundarban-biosphere-reserve-sbr-india" class="btn btn-primary btn-sm">Procedia</a> <a href="https://publications.waset.org/abstracts/164722.pdf" target="_blank" class="btn btn-primary btn-sm">PDF</a> <span class="bg-info text-light px-1 py-1 float-right rounded"> Downloads <span class="badge badge-light">151</span> </span> </div> </div> <div class="card paper-listing mb-3 mt-3"> <h5 class="card-header" style="font-size:.9rem"><span class="badge badge-info">4</span> Mobulid Ray Post-Release Mortality to Assess the Feasibility of Live-Release Management Measures</h5> <div class="card-body"> <p class="card-text"><strong>Authors:</strong> <a href="https://publications.waset.org/abstracts/search?q=Sila%20K.%20Sari">Sila K. Sari</a>, <a href="https://publications.waset.org/abstracts/search?q=Betty%20J.L.%20Laglbauer"> Betty J.L. Laglbauer</a>, <a href="https://publications.waset.org/abstracts/search?q=Muhammad%20G.%20Salim"> Muhammad G. Salim</a>, <a href="https://publications.waset.org/abstracts/search?q=Irianies%20C.%20Gozali"> Irianies C. Gozali</a>, <a href="https://publications.waset.org/abstracts/search?q=Iqbal%20Herwata"> Iqbal Herwata</a>, <a href="https://publications.waset.org/abstracts/search?q=Fahmi%20Fahmi"> Fahmi Fahmi</a>, <a href="https://publications.waset.org/abstracts/search?q=Selvia%20Oktaviyani"> Selvia Oktaviyani</a>, <a href="https://publications.waset.org/abstracts/search?q=Isabel%20Ender"> Isabel Ender</a>, <a href="https://publications.waset.org/abstracts/search?q=Sarah%20%20Lewis"> Sarah Lewis</a>, <a href="https://publications.waset.org/abstracts/search?q=Abraham%20Sianipar"> Abraham Sianipar</a>, <a href="https://publications.waset.org/abstracts/search?q=Mark%20Erdmann"> Mark Erdmann</a> </p> <p class="card-text"><strong>Abstract:</strong></p> Taking strides towards the sustainable use of marine stocks requires science-based management of target fish populations and reduction of bycatch in non-selective fisheries. Among elasmobranchs, mobulid rays are faced with high extinction risk due to intrinsic vulnerability to fishing and their conservation has been recognized as a strong priority both in Indonesia and worldwide. Despite their common vulnerabilities to fishing pressure due to slow growth, late maturation and low fecundity, only manta rays, but not devil rays, are protected in Indonesian waters. However, both manta and devil rays are captured in non-selective fisheries, in particular drift gillnets, since their habitat overlaps with fishing grounds for primary target species (e.g. marlin, swordfish and bullet tuna off the coast of Muncar). For this reason, mobulid populations are being heavily impacted, and while national-level protections are crucial to help conservation, they may not suffice alone to insure populations sustainability. In order to assess the potential of applying live-release management measures to conserve mobulids captured as bycatch in drift gillnets, we deployed pop-up survival archival transmitters to assess post-release mortality in Indonesian mobulid rays. We also assessed which fishing practices, in particular, soak duration, affected post-release mortality in order to draw relevant conclusions for management. <p class="card-text"><strong>Keywords:</strong> <a href="https://publications.waset.org/abstracts/search?q=Mobulid" title="Mobulid">Mobulid</a>, <a href="https://publications.waset.org/abstracts/search?q=Devil%20ray" title=" Devil ray"> Devil ray</a>, <a href="https://publications.waset.org/abstracts/search?q=Manta%20ray" title=" Manta ray"> Manta ray</a>, <a href="https://publications.waset.org/abstracts/search?q=Bycatch" title=" Bycatch"> Bycatch</a> </p> <a href="https://publications.waset.org/abstracts/120119/mobulid-ray-post-release-mortality-to-assess-the-feasibility-of-live-release-management-measures" class="btn btn-primary btn-sm">Procedia</a> <a href="https://publications.waset.org/abstracts/120119.pdf" target="_blank" class="btn btn-primary btn-sm">PDF</a> <span class="bg-info text-light px-1 py-1 float-right rounded"> Downloads <span class="badge badge-light">172</span> </span> </div> </div> <div class="card paper-listing mb-3 mt-3"> <h5 class="card-header" style="font-size:.9rem"><span class="badge badge-info">3</span> Mobulid Ray Fishery Characteristics and Trends in East Java to Inform Management Decisions</h5> <div class="card-body"> <p class="card-text"><strong>Authors:</strong> <a href="https://publications.waset.org/abstracts/search?q=Muhammad%20G.%20Salim">Muhammad G. Salim</a>, <a href="https://publications.waset.org/abstracts/search?q=Betty%20J.L.%20Laglbauer"> Betty J.L. Laglbauer</a>, <a href="https://publications.waset.org/abstracts/search?q=Sila%20K.%20Sari"> Sila K. Sari</a>, <a href="https://publications.waset.org/abstracts/search?q=Irianes%20C.%20Gozali"> Irianes C. Gozali</a>, <a href="https://publications.waset.org/abstracts/search?q=Fahmi"> Fahmi</a>, <a href="https://publications.waset.org/abstracts/search?q=Didik%20Rudianto"> Didik Rudianto</a>, <a href="https://publications.waset.org/abstracts/search?q=Selvia%20Oktaviyani"> Selvia Oktaviyani</a>, <a href="https://publications.waset.org/abstracts/search?q=Isabel%20Ender"> Isabel Ender </a> </p> <p class="card-text"><strong>Abstract:</strong></p> Muncar, East Java, is one of the largest artisanal fisheries in Indonesia. Sharks and rays are caught as both target and bycatch, for local meat consumption and with some derived products exported. Of the seven mobulid ray species occurring in Indonesia, five have been recorded as retained bycatch at Muncar fishing port: the spinetail devil ray (Mobula mobular), the bentfin devil ray (Mobula thurstoni), the sicklefin devil ray (Mobula tarapacana), the oceanic manta ray (Mobula birostris) and the reef manta ray (Mobula alfredi). Both manta ray species are listed as Vulnerable by the International Union for the Conservation of Nature and are protected in Indonesia despite still being captured as bycatch, while all the three devil ray species mentioned here are listed as Endangered and do not currently benefit from any protection in Indonesian waters. Mobulid landings in East Java are caused primarily by small-scale drift gillnets but they also occasionally occur on longlines and in purse-seines operating off the coast of East Java and occasionally in fishing grounds located as far as the Makassar and Sumba Straits. Landing trends from 2015-2019 (non-continuous surveys) revealed that the highest abundance of mobulid rays at Muncar fishing port occurs during the upwelling season from June-October. During El-Nino or above-average temperature years, this may extend until November (such as in 2015 and 2019). The strong seasonal upwelling along the East Java coast is linked to higher zooplankton abundance (inferred from chlorophyll-a sea-surface concentrations), on which mobulids forage, along with teleost fishes constituting the primary target of gillnet fisheries in the Bali Strait. Mobulid ray landings in Muncar were dominated by Mobula mobular, followed by M. thurstoni, M. tarapacana, M. birostris and M. alfredi, however, the catch varied across years and seasons. A majority of immature individuals were recorded in M. mobular and M. thurstoni, and slight decreases in landings, despite no known changes in fishing effort, were observed across the upwelling seasons of 2015-2018 for M. mobular. While all mobulids are listed on Appendix II of the Convention on International Trade in Endangered Species, which regulates international trade in gill plates sought after in the Chinese Medicine Trade, local and national-level management measures are required to sustain mobulid populations. The findings presented here provide important baseline data, from which potential management approaches can be identified. <p class="card-text"><strong>Keywords:</strong> <a href="https://publications.waset.org/abstracts/search?q=devil%20ray" title="devil ray">devil ray</a>, <a href="https://publications.waset.org/abstracts/search?q=mobulid" title=" mobulid"> mobulid</a>, <a href="https://publications.waset.org/abstracts/search?q=manta%20ray" title=" manta ray"> manta ray</a>, <a href="https://publications.waset.org/abstracts/search?q=Indonesia" title=" Indonesia"> Indonesia</a> </p> <a href="https://publications.waset.org/abstracts/125539/mobulid-ray-fishery-characteristics-and-trends-in-east-java-to-inform-management-decisions" class="btn btn-primary btn-sm">Procedia</a> <a href="https://publications.waset.org/abstracts/125539.pdf" target="_blank" class="btn btn-primary btn-sm">PDF</a> <span class="bg-info text-light px-1 py-1 float-right rounded"> Downloads <span class="badge badge-light">178</span> </span> </div> </div> <div class="card paper-listing mb-3 mt-3"> <h5 class="card-header" style="font-size:.9rem"><span class="badge badge-info">2</span> Importance of the Bali Strait for Devil Ray Reproduction </h5> <div class="card-body"> <p class="card-text"><strong>Authors:</strong> <a href="https://publications.waset.org/abstracts/search?q=Irianes%20C.%20Gozali">Irianes C. Gozali</a>, <a href="https://publications.waset.org/abstracts/search?q=Betty%20J.L.%20%20Laglbauer"> Betty J.L. Laglbauer</a>, <a href="https://publications.waset.org/abstracts/search?q=Muhammad%20%20G.%20Salim"> Muhammad G. Salim</a>, <a href="https://publications.waset.org/abstracts/search?q=Sila%20%20K.%20Sari"> Sila K. Sari</a>, <a href="https://publications.waset.org/abstracts/search?q=Fahmi%20Fahmi"> Fahmi Fahmi</a>, <a href="https://publications.waset.org/abstracts/search?q=Selvia%20Oktaviyani"> Selvia Oktaviyani</a> </p> <p class="card-text"><strong>Abstract:</strong></p> Muncar, located off the eastern coast of Java, is an important fishing port for small-scale fleets which land mobulid rays as retained bycatch, primarily in drift gillnets. Due to overlap with fishing grounds in the Bali Strait, three devil ray species are landed in Muncar, the spinetail devil ray Mobula mobular, the bentfin devil ray Mobula thurstoni, and the Chilean devil ray Mobula tarapacana, which are all listed as Endangered by the International Union for the Conservation of Nature. However, despite the importance of life-history data to better manage stocks, such information is still rare or unavailable for Indonesian mobulid ray populations. Using morphometric data, reproductive assessments, and samples collected from dead specimens at fish markets from 2015-2019, we provide information on the maturity stage, reproductive periodicity, gestation, and size at parturition. A majority of immature individuals of all three devil ray species were recorded (<10% individuals in Mobula mobular to <30% individuals in Mobula thurstoni). Pregnant females of two species, Mobula mobular and Mobula thurstoni were recorded containing embryos of various developmental stages (each with a single embryo in the left functional uterus), while for Mobula tarapacana, no fetuses were found. The largest embryo recorded in M. mobular was within the range of that previously reported for neonates of the species in Indonesia (957 cm, for a 920-994 range), and represents a near-term embryo reflecting size at parturition. Low reproductive output was confirmed for the study-species. Based on this study, we infer that the Bali Straight is likely an important location for devil ray reproduction, which raises concern for the sustainability of mobulid ray populations in the face of bycatch in drift gillnets. Potential management approaches to tackle this issue are discussed. <p class="card-text"><strong>Keywords:</strong> <a href="https://publications.waset.org/abstracts/search?q=devil%20ray" title="devil ray">devil ray</a>, <a href="https://publications.waset.org/abstracts/search?q=mobulid" title=" mobulid"> mobulid</a>, <a href="https://publications.waset.org/abstracts/search?q=reproduction" title=" reproduction"> reproduction</a>, <a href="https://publications.waset.org/abstracts/search?q=Indonesia" title=" Indonesia"> Indonesia</a> </p> <a href="https://publications.waset.org/abstracts/120076/importance-of-the-bali-strait-for-devil-ray-reproduction" class="btn btn-primary btn-sm">Procedia</a> <a href="https://publications.waset.org/abstracts/120076.pdf" target="_blank" class="btn btn-primary btn-sm">PDF</a> <span class="bg-info text-light px-1 py-1 float-right rounded"> Downloads <span class="badge badge-light">182</span> </span> </div> </div> <div class="card paper-listing mb-3 mt-3"> <h5 class="card-header" style="font-size:.9rem"><span class="badge badge-info">1</span> Conservation of Sea Turtle in Cox’s Bazar- Teknaf Peninsula and Sonadia Island Ecologically Critical Area (ECA) of Bangladesh</h5> <div class="card-body"> <p class="card-text"><strong>Authors:</strong> <a href="https://publications.waset.org/abstracts/search?q=Pronob%20Kumar%20Mozumder%20M.%20Nazrul%20Islam">Pronob Kumar Mozumder M. Nazrul Islam</a>, <a href="https://publications.waset.org/abstracts/search?q=M.%20Abdur%20Rob%20Mollah"> M. Abdur Rob Mollah</a> </p> <p class="card-text"><strong>Abstract:</strong></p> This study was conducted in Cox’s Bazar-Teknaf Peninsula and Sonadia Island Ecologically Critical Areas during the period of October, 2011 to June, 2013. Six species of marine turtle are found in the Indian Ocean. Among them, olive ridley (Lepidochelys olivacea) listed as endangered in the IUCN Red List of Threatened Species. Marine turtle populations in the Indian Ocean have been depleted through long-term exploitation of eggs and adults, incidental capture (fisheries bycatch) and many other sources of mortality. The specific objective of the study was to conserve the sea turtles specially the olive ridley (Lepidochelys olivacea) with a view to contribute towards protection of the turtle species from extinction and to facilitate hatching of eggs through providing protection to turtle eggs or nest through ex-situ conservation efforts. In order to achieve the desired outputs and success, a total of five turtle hatcheries were established at Pechardwip, Khurermukh, Hazompara, Bodormokam, and Sonadia Eastpara sites. In total, 31,853 eggs were collected from 260 nests and were transferred to five hatcheries. The number of eggs/nest varied from 38 to 190 with an average clutch size of 122 eggs/ nest. Hatching of eggs took place during January to June with a peak in April. Sea turtle eggs were incubated by metabolic heat and the heat of the sun. The incubation period of turtle eggs in Cox’s Bazar-Teknaf Peninsula and Sonadia Island ECAs extended from 54 to 75 days depending on the month with an average of 66 days. During study period the temperature in the ECAs varied between 10.5-34.5°C. A total of 27,937 hatchlings of turtle were produced from the five hatcheries and all the hatchlings produced were released into the sea. Hatching rates varied from 74-98 % depending on the location and months with an average of 88 %. Sea turtles spend the majority of their lives in the sea, only emerging on beaches to nest. Despite the intense conservation efforts on the beaches, some populations have still declined to the edge of extinction. So proper conservation and awareness measure should be taken for prevention of turtle extinction. <p class="card-text"><strong>Keywords:</strong> <a href="https://publications.waset.org/abstracts/search?q=conservation%20of%20sea%20turtle" title="conservation of sea turtle">conservation of sea turtle</a>, <a href="https://publications.waset.org/abstracts/search?q=Bangladesh" title=" Bangladesh"> Bangladesh</a>, <a href="https://publications.waset.org/abstracts/search?q=ecologically%20critical%20area" title=" ecologically critical area"> ecologically critical area</a>, <a href="https://publications.waset.org/abstracts/search?q=ECA" title=" ECA"> ECA</a>, <a href="https://publications.waset.org/abstracts/search?q=Lepidochelys%20olivacea" title=" Lepidochelys olivacea"> Lepidochelys olivacea</a> </p> <a href="https://publications.waset.org/abstracts/19016/conservation-of-sea-turtle-in-coxs-bazar-teknaf-peninsula-and-sonadia-island-ecologically-critical-area-eca-of-bangladesh" class="btn 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