Fish Aggregating Device (FAD)
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Oeconomics of the Philippine Small Pelagics Fishery
l1~~iJlLll.I.~lJ~ - r--I ~ ~~.mr'l ~ SH I 207 TR4 . #38c~.1 .I @)~~[fi]C!ffi]m @U00r@~O~~[ro)~[fi@ \ . §[fi]~~~~~~ ~~ II "'-' IDi III ~~- ~@1~ ~(;1~ ~\YL~ (b~ oeconomics of the Philippine Small Pelagics Fishery Annabelle C. ad Robert S. Pomeroy Perlita V. Corpuz Max Agiiero INTERNATIONAL CENTER FOR LIVING AQUATIC RESOURCES MANAGEMENT MANILA, PHILIPPINES 407 Biqeconomics of the Philippine Small Pelagics Fishery 7?kq #38 @-,,/ JAW 3 1 1996 Printed in Manila, Philippines Published by the International Center for Living Aquatic Resources Management, MCPO Box 2631, 0718 Makati, Metro Manila, Philippines Citation: Trinidad, A.C., R.S. Pomeroy, P.V. Corpuz and M. Aguero. 1993. Bioeconomics of the Philippine small pelagics fishery. ICLARM Tech. Rep. 38, 74 p. ISSN 01 15-5547 ISBN 971-8709-38-X Cover: Municipal ringnet in operation. Artwork by O.F. Espiritu, Jr. ICLARM Contribution No. 954 CONTENTS Foreword ................................................................................................................................v Abstract ..............................................................................................................................vi Chapter 1. Introduction ......................................................................................................1 Chapter 2 . Description of the Study Methods ................................................................4 Data Collection ....................................................................................................................4 Description -
Drifting Fish Aggregating Devices (Fads) Deploying, Soaking and Setting – When Is a FAD ‘Fishing’?
THE INTERNATIONAL JOURNAL OF MARINE The International Journal of AND COASTAL Marine and Coastal Law 34 (2019) 731–754 LAW brill.com/estu Drifting Fish Aggregating Devices (FADs) Deploying, Soaking and Setting – When is a FAD ‘Fishing’? Quentin Hanich,a Ruth Davis,a Glen Holmes,b Elizabeth-Rose Amidjogbea and Brooke Campbella a Australian National Centre for Ocean Resources and Security (ANCORS), University of Wollongong, Wollongong, NSW, Australia b GH Consulting Services, Brisbane, Queensland, Australia [email protected]; [email protected]; [email protected]; [email protected]; [email protected] Abstract This article describes the proliferation of drifting fish aggregating devices (FADs) and analyses subsequent legal questions that arise for fisheries and marine litter manage- ment over who is responsible for FADs during their drifting stage. This follows recent concerns about unlicensed FADs drifting through closed areas. This article analyses a case study of the Western and Central Pacific Fisheries Commission (WCPFC) in order to determine State obligations to manage drifting FADs. Analysis concludes that a drifting FAD in the WCPFC Area is ‘fishing’ from deployment to recovery, thereby creat- ing obligations to monitor, control and report drifting FADs, consistent with broader obligations for coastal and flag States. The article recommends strengthening regional management in three ways: implement regional drifting FAD monitoring systems; con- trol deployment of drifting FADs so as to promote recovery and minimize lost gear; -
Tuna Fishing and a Review of Payaos in the Philippines
Session 1 - Regional syntheses Tuna fishing and a review of payaos in the Philippines Jonathan O. Dickson*1', Augusto C. Nativiclacl(2) (1) Bureau of Fisheries and Aquatic Resources, 860 Arcadia Bldg., Quezon Avenue, Quezon City 3008, Philippines - [email protected] (2) Frabelle Fishing Company, 1051 North Bay Blvd., Navotas, Metro Manila, Philippines Abstract Payao is a traditional concept, which has been successfully commercialized to increase the landings of several species valuable to the country's export and local industries. It has become one of the most important developments in pelagic fishing that significantly contributed to increased tuna production and expansion of purse seine and other fishing gears. The introduction of the payao in tuna fishing in 1975 triggered the rapid development of the tuna and small pelagic fishery. With limited management schemes and strategies, however, unstable tuna and tuna-like species production was experienced in the 1980s and 1990s. In this paper, the evolution and development of the payao with emphasis on the technological aspect are reviewed. The present practices and techniques of payao in various parts of the country, including its structure, ownership, distribution, and fishing operations are discussed. Monitoring results of purse seine/ringnet operations including handline using payao in Celebes Sea and Western Luzon are presented to compare fishing styles and techniques, payao designs and species caught. The fishing gears in various regions of the country for harvesting payao are enumerated and discussed. The inshore and offshore payaos in terms of sea depth, location, designs, fishing methods and catch composi- tion are also compared. Fishing companies and fisherfolk associations involved in payao operation are presented to determine extent of uti- lization and involvement in the municipal and commercial sectors of the fishing industry. -
Highest Risk Abandoned, Lost and Discarded Fishing Gear
www.nature.com/scientificreports OPEN Highest risk abandoned, lost and discarded fshing gear Eric Gilman1*, Michael Musyl2, Petri Suuronen3, Milani Chaloupka4, Saeid Gorgin5, Jono Wilson1,6 & Brandon Kuczenski6 Derelict abandoned, lost and discarded fshing gear have profound adverse efects. We assessed gear-specifc relative risks from derelict gear to rank-order fshing methods based on: derelict gear production rates, gear quantity indicators of catch weight and fshing grounds area, and adverse consequences from derelict gear. The latter accounted for ghost fshing, transfer of microplastics and toxins into food webs, spread of invasive alien species and harmful microalgae, habitat degradation, obstruction of navigation and in-use fshing gear, and coastal socioeconomic impacts. Globally, mitigating highest risk derelict gear from gillnet, tuna purse seine with fsh aggregating devices, and bottom trawl fsheries achieves maximum conservation gains. Locally, adopting controls following a sequential mitigation hierarchy and implementing efective monitoring, surveillance and enforcement systems are needed to curb derelict gear from these most problematic fsheries. Primary and synthesis research are priorities to improve future risk assessments, produce the frst robust estimate of global derelict gear quantity, and assess the performance of initiatives to manage derelict gear. Findings from this frst quantitative estimate of gear-specifc relative risks from derelict gear guide the allocation of resources to achieve the largest improvements from mitigating adverse efects of derelict gear from the world’s 4.6 million fshing vessels. Over the past decade there has been increasing international recognition of the need for multilateral eforts to address transboundary adverse ecological and socioeconomic efects of abandoned, lost and discarded fshing gear (ALDFG), also called derelict fshing gear 1, 2. -
Print 1990-05-14 Symp Artificial Reefs for Management of Marine
INDONESIA'S EXPERIENCE OF FISH AGGREGATING DEVICES (FADS) BY HARDJONO' 1. INTRODUCTION As an archipelagic state, Indonesia is endowed with a vast area of marine waters amounting to 5.8 million km, comprising 2.8 million km of internal waters, 0.3 million km of territorial waters, and 2.7 million km of Exclusive Economic Zone (EEZ). Large areas of marine waters in Indonesia offer good resource potential typical of the tropics and marine fisheries play an important role in the Indonesia fisheries. Among the multispecies tropical resources available in Indonesia waters those of great value are skipjack, tuna, promfret, Spanish mackerel, snapper, grouper and some carangids. Among shellfish, shrimp (Penaeus sp.) and spiny lobster are the most expensive. Recent estimates of the fisheries potentials of the country indicate a.potentia1 reaching 6.6 million mt, comprising of 4.5 million mt ib archipelagic and territorial waters and 2.1 million mt in the EEZ. The development of marine fish production in Indonesia during the the years 1980-1987 shows an average increase of 6.22% a year. At present marine fisheries contribute 76% of the total fisheries production which by 1987 reached 2.017 million mt. As a result of diverse characteristics of the Indonesian archipelago, the country's marine fisheries are complex and varied, and are dominated by traditional fishing activities operating a large number of very small vessels. Various kinds of fishing gear are employed which are dominated by gill nets comprising nearly one third of all fishing units operated. When the amount of fish landed by different types of fishing gear is considered, payang: and purse seine contribute the largest part of fish landed amounting to about 26% of total annual fish landings. -
Assessing the Number of Moored Fishing Aggregating Devices Through Aerial Surveys: a Case Study from Guadeloupe
1 Fisheries Research Achimer January 2017, Volume 185 Pages 73-82 http://dx.doi.org/10.1016/j.fishres.2016.10.003 http://archimer.ifremer.fr http://archimer.ifremer.fr/doc/00355/46605/ © 2016 Elsevier B.V. All rights reserved. Assessing the number of moored fishing aggregating devices through aerial surveys: A case study from Guadeloupe Guyader Olivier1, *, Bauer Robert 2, Reynal Lionel 3 1 Ifremer, Univ Brest, CNRS, UMR 6308, AMURE, Unité d’Economie Maritime, IUEM, F-29280 Plouzane, France 2 Ifremer, UMR Marbec, Avenue Jean Monnet, CS 30171, 34203 Sète Cedex, France 3 Ifremer, Unité Biodiversité et Environnement, Département Ressources Biologiques et Environnement (RBE), Délégation de Martinique 79 Route de Pointe-Fort, 97231 Le Robert, Martinique * Corresponding author : Olivier Guyader, email address : [email protected] Abstract : Moored fish aggregating devices (MFADs) are increasingly being used in small-scale tropical fisheries to access pelagic fish species that are otherwise difficult to harvest in large numbers. Little attention has yet been paid to monitoring MFADs in coastal areas, however. This is most likely due to the small-scale nature of most fisheries that utilize them and the presumed lower impact of those fisheries on fish stocks and their ecosystems. In this paper, we examined the abundance and density of MFADs around Guadeloupe, using aerial line transect surveys. Estimated MFAD densities were found to be high compared with previously reported densities in this area, especially within the 22–45 km range offshore. We examine and discuss possible reasons for these high densities. The main drivers appear to be the target species dolphinfish (Coryphaena hippurus) and yellowfin tuna (Thunnus albacares) and related fishing behaviour. -
Victorian Fish Aggregation Devices
Photos courtesy of NSW Fisheries Victorian Fish Aggregation Devices Feasibility Assessment and Concept Design Recreational Fishing Grants Program Research Report Victorian Fish Aggregation Devices Feasibility Assessment and Concept Design Project number: RFGP/11/12/13 March 2013 Recreational Fishing Grants Program Research Report If you would like to receive this information/publication in an accessible format (such as large print or audio) please call the Customer Service Centre on 136 186, TTY 1800 122 969, or email [email protected]. Published by the Department of Primary Industries Fisheries Victoria, March 2013 © The State of Victoria 2013. This publication is copyright. No part may be reproduced by any process except in accordance with the provisions of the Copyright Act 1968. Preferred way to cite this publication: Green C. P. Victorian Fish Aggregation Devices - Feasibility Assessment and Concept Design. Recreational Fishing Grant Program – Research Report. Department of Primary Industries, Victoria ISBN 978-1-74326-414-0 (print) 978-1-74326-415-7 (online) Copies are available from the website: www.dpi.vic.gov.au/fishing Authorised by the Department of Primary Industries 1 Spring Street, Melbourne 3000. Author Attribution: Please contact Dr Corey Green (03) 5258 0111 for information on this project. Disclaimer This publication may be of assistance to you but the State of Victoria and its employees do not guarantee that the publication is without flaw of 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. -
Use of Video Monitoring to Quantify Spatial and Temporal Patterns in Fishing Activity Across Sectors at Moored Fish Aggregating Devices Off Puerto Rico
SCIENTIA MARINA 82(2) June 2018, 107-117, Barcelona (Spain) ISSN-L: 0214-8358 https://doi.org/10.3989/scimar.04730.09A Use of video monitoring to quantify spatial and temporal patterns in fishing activity across sectors at moored fish aggregating devices off Puerto Rico Wessley Merten 1, Roberto Rivera 2, Richard Appeldoorn 3, Kelvin Serrano 4, Omar Collazo 4, Nilda Jimenez 4 1 Collaborative FAD Research Programme, Beyond Our Shores, Inc., PO Box 662, Rockville, MD 20848, USA. (WM) (Corresponding author) E-mail: [email protected]. ORCID iD: https://orcid.org/0000-0001-8746-0058 2 College of Business, University of Puerto Rico Mayagüez, PO Box 9000, Mayagüez, PR 00681, USA. (RR) E-mail: [email protected]. ORCID iD: https://orcid.org/0000-0003-2890-6966 3 Department of Marine Sciences, University of Puerto Rico, Mayagüez, PO Box 9000, Mayagüez, PR 00681, USA. (RA) E-mail: [email protected]. ORCID iD: https://orcid.org/0000-0003-2179-7496 4 Puerto Rico Department of Natural and Environmental Resources, Fish and Wildlife Bureau, Marine Ecology Division, PO Box 366147, SJ, PR 00926, USA. (KS) E-mail: [email protected]. ORCID iD: https://orcid.org/0000-0001-5963-193X (OC) E-mail: [email protected]. ORCID iD: https://orcid.org/0000-0003-2478-7285 (NJ) E-mail: [email protected]. ORCID iD: https://orcid.org/0000-0001-7515-8951 Summary: A key challenge in small-scale fisheries that use moored fish aggregating devices (mFADs) is the ability to accurately quantify multi-sector fishing activity through fishery-independent methods. -
Fish Aggregating Devices (Fads) Prathibha Rohit Principal Scientist, Pelagic Fisheries Division CMFRI Research Centre, Mangalore P.B
Fish aggregating devices (FADs) Prathibha Rohit Principal Scientist, Pelagic Fisheries Division CMFRI Research Centre, Mangalore P.B. 244, Mangalore, Karnataka-575 001 Fish aggregating devices, more commonly called FADs, are anchored or drifting objects that are placed in the ocean to attract fish. They may be a permanent, semi-permanent or temporary structure or device made from any material and used to lure fish. They have been used for thousands of years in various forms. The earliest surface/ midwater FADs were elements from nature such as driftwood and trees. Fishermen from Indonesia and Philippines began building floating rafts of bamboo and other materials to attract fish as early as 1900. Now surface and midwater artificial FADs are systematically used in a large number of countries. Present practices vary considerably, sometimes involving advanced technology. Traditional FADs, based on long-term fishing experience, are made on-the-spot with local materials and used in shallow coastal waters (depth 50-200 m) by small-scale fishers to catch small pelagic fish and bait, e.g. payaos (Philippines), unjang (Malaysia), rumpon (Indonesia). Modern FADs, the result of imported technology and materials, can be anchored to over 3000 m. Drifting FADs are not tethered to the bottom and can be natural objects such as logs or man-made. Certain models have large surface dimensions. Moored FADs occupy a fixed location and attach to the sea bottom using a weight such as a concrete block. A rope made of floating synthetics such as polypropylene attaches to the mooring and in turn attaches to a buoy. The buoy can float at the surface (lasting 3–4 years) or lie subsurface (mid water FAD) to avoid detection and surface hazards such as weather and ship traffic. -
Fish Aggregating Devices Drift Like Oceanographic Drifters in the Near-Surface Currents of the Atlantic and Indian Oceans
Fish aggregating devices drift like oceanographic drifters in the near-surface currents of the Atlantic and Indian Oceans T. Imzilena, E. Chassotb, J. Bardec, H. Demarcqa, A. Maufroya,d, L. Roa-Pascualia, J-F. Ternona, C. Lette,∗ aMARBEC, IRD, Ifremer, Univ Montpellier, CNRS, S`ete,France bIRD, Seychelles Fishing Authority, PO BOX 449, Victoria, Seychelles cInstitut de Recherche pour le D´eveloppement (IRD), Indian Ocean Commission, Eb`ene,´ Mauritius dORTHONGEL, 11 bis rue des sardiniers, 29 900 Concarneau, France eIRD, Sorbonne Universit´e,UMMISCO, F-93143, Bondy, France Abstract Knowledge of ocean surface dynamics is crucial for oceanographic and cli- mate research. The satellite-tracked movements of hundreds of drifters de- ployed by research and voluntary observing vessels provide high-frequency and high-resolution information on near-surface currents around the globe. Consequently, they constitute a major component of the Global Ocean Ob- serving System (GOOS). However, maintaining this array is costly and in some oceanic regions such as the tropics, spatio-temporal coverage is lim- ited. Here, we demonstrate that the GPS-buoy equipped fish aggregating devices (FADs) used in tropical tuna fisheries to increase fishing success are also capable of providing comparable near-surface current information. We analyzed millions of position data collected between 2008 and 2014 from more than 15,000 FADs and 2,000 drifters, and combined this information with remotely-sensed near-surface current data to demonstrate that the sur- face velocity components of FADs and drifters are highly correlated in the Atlantic and Indian Oceans. While it was noted that the subsurface struc- tures of FADs did slow them down relative to the drifters, particularly in the Atlantic Ocean, this bias was measurable and could be accounted for ∗Corresponding author Email address: [email protected] (C. -
2018 Lionfish Summit Report
2018 Lionfish Summit October 2-4, 2018 Cocoa Beach, Florida Hosted by the Florida Fish and Wildlife Conservation Commission Table of Contents Media and Resources…………………………………………………………………………………………………….…………. 2 Introduction……………………………………………………………………………………..……………………………………… 3 Theme I: Policy and Regulations……………………………………………………………..……………………..…….….. 6 Theme II: Control Efforts/Research and Monitoring………………………………………………………..……… 11 Theme III: Outreach and Education…………………………………………………………………………………..……. 18 Future Directions……………………………………………………………………………………………………………….…… 23 Appendix A: Lionfish Summit Agenda……………………………………………………………………………….……. 24 Appendix B: Presentation Abstracts…………………………………………………………………………………….…. 28 Appendix C: iClicker Survey Results……………………………………..…………………..………….…………………. 65 Appendix D: Evaluations…………………………………………………………………………………….…………………… 66 Appendix E: Attendee List………………………………………………………………………………………………….…… 67 Appendix F: FWC Lionfish Program Overview 2014 – 2018……………………………….……………………. 72 1 | P a g e Media and Resources ▪ View photos in the Lionfish Summit Flickr album. ▪ Live video footage broadcast by the Florida Channel: o 10/02/18 Florida Fish and Wildlife Conservation Commission Lionfish Summit o 10/03/18 Florida Fish and Wildlife Conservation Commission Lionfish Summit Part 1 o 10/03/18 Florida Fish and Wildlife Conservation Commission Lionfish Summit Part 2 ▪ Video recordings of the oral presentations are available upon request by contacting [email protected]. ▪ Visit MyFWC.com/Lionfish or FWCReefRangers.com for agency information -
RECENT USE of FISH AGGREGATING DEVICES in the EASTERN TROPICAL PACIFIC TUNA PURSE-SEINE FISHERY: 1990-1994 (Revised March 1996)
RECENT USE OF FISH AGGREGATING DEVICES IN THE EASTERN TROPICAL PACIFIC TUNA PURSE-SEINE FISHERY: 1990-1994 (Revised March 1996) (This is a revised copy of Administrative Report LJ-95-14) By Wesley A. Armstrong and Charles W. Oliver Southwest Fisheries Science Center P.O. Box 271 La Jolla, California 92038-0271 March 1996 ADMINISTRATIVE REPORT LJ-96-02 Contents Page List of Figures....................................................................................................................................ii List of Tables.................................................................................................................................... iii INTRODUCTION............................................................................................................................1 LOGS ...............................................................................................................................................2 FADS................................................................................................................................................4 FAD INVESTIGATIONS: 1990-1992 .............................................................................................6 FAD INVESTIGATIONS: 1993-1994 .............................................................................................7 DOLPHIN-SAFE QUESTIONNAIRE.............................................................................................8 SKIPPER A's FADs: Drifting FADs: Construction and Deployment..........................................................................9