Longline Fisheries and Foraging Distribution of Flesh-Footed Shearwaters in Eastern Australia
Incidental seabird mortality associated with bycatch during longline commercial fishing is a conservation concern. An initial step to estimating likelihood of seabird bycatch and conceiving conservation strategies is determining amount of overlap between foraging birds and commercial fishing effort,...
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Published in | The Journal of wildlife management Vol. 73; no. 3; pp. 399 - 406 |
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Main Authors | , , , |
Format | Journal Article |
Language | English |
Published |
Oxford, UK
The Wildlife Society
01.04.2009
Blackwell Publishing Ltd |
Subjects | |
Online Access | Get full text |
ISSN | 0022-541X 1937-2817 |
DOI | 10.2193/2007-461 |
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Abstract | Incidental seabird mortality associated with bycatch during longline commercial fishing is a conservation concern. An initial step to estimating likelihood of seabird bycatch and conceiving conservation strategies is determining amount of overlap between foraging birds and commercial fishing effort, identifying oceanographic features associated with foraging birds, and quantifying dive characteristics. We tracked 24 adult flesh-footed shearwaters (Puffinus carneipes) breeding on Lord Howe Island located east of Australia during incubation and early and late chick-rearing periods from 6 January to 17 April 2005. At-sea foraging distribution of flesh-footed shearwaters was primarily confined within the jurisdictional Australian Fishing Zone. Foraging was strongly associated with sea-surface temperature >24° C. Spatial and temporal overlap of longline fishing with foraging shearwaters varied throughout the breeding season, but was greatest (63% overlap) during early chick-rearing. Mean maximum distance reached from the breeding colony during a foraging event was 804 km (SD = 280) from Lord Howe Island. Foraging behavior was strongly diurnal, with 91% of dives occurring during daylight, and most dives (77%) were <5 m. Given that longline fishing and flesh-footed shearwaters overlap substantially, the Australian Fisheries Management Authority should consider implementing additional regulations to further reduce bycatch. Conservation strategies such as setting longlines at nights may reduce flesh-footed shearwater bycatch. |
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AbstractList | Incidental seabird mortality associated with bycatch during longline commercial fishing is a conservation concern. An initial step to estimating likelihood of seabird bycatch and conceiving conservation strategies is determining amount of overlap between foraging birds and commercial fishing effort, identifying oceanographic features associated with foraging birds, and quantifying dive characteristics. We tracked 24 adult flesh-footed shearwaters (Puffinus carneipes) breeding on Lord Howe Island located east of Australia during incubation and early and late chick-rearing periods from 6 January to 17 April 2005. At-sea foraging distribution of flesh-footed shearwaters was primarily confined within the jurisdictional Australian Fishing Zone. Foraging was strongly associated with sea-surface temperature >24°C. Spatial and temporal overlap of longline fishing with foraging shearwaters varied throughout the breeding season, but was greatest (63% overlap) during early chick-rearing. Mean maximum distance reached from the breeding colony during a foraging event was 804 km (SD = 280) from Lord Howe Island. Foraging behavior was strongly diurnal, with 91% of dives occurring during daylight, and most dives (77%) were <5 m. Given that longline fishing and flesh-footed shearwaters overlap substantially, the Australian Fisheries Management Authority should consider implementing additional regulations to further reduce bycatch. Conservation strategies such as setting longlines at nights may reduce fleshfooted shearwater bycatch. Incidental seabird mortality associated with bycatch during longline commercial fishing is a conservation concern. An initial step to estimating likelihood of seabird bycatch and conceiving conservation strategies is determining amount of overlap between foraging birds and commercial fishing effort, identifying oceanographic features associated with foraging birds, and quantifying dive characteristics. We tracked 24 adult flesh-footed shearwaters (Puffinus carneipes) breeding on Lord Howe Island located east of Australia during incubation and early and late chick-rearing periods from 6 January to 17 April 2005. At-sea foraging distribution of flesh-footed shearwaters was primarily confined within the jurisdictional Australian Fishing Zone. Foraging was strongly associated with sea-surface temperature >24° C. Spatial and temporal overlap of longline fishing with foraging shearwaters varied throughout the breeding season, but was greatest (63% overlap) during early chick-rearing. Mean maximum distance reached from the breeding colony during a foraging event was 804 km (SD = 280) from Lord Howe Island. Foraging behavior was strongly diurnal, with 91% of dives occurring during daylight, and most dives (77%) were <5 m. Given that longline fishing and flesh-footed shearwaters overlap substantially, the Australian Fisheries Management Authority should consider implementing additional regulations to further reduce bycatch. Conservation strategies such as setting longlines at nights may reduce flesh-footed shearwater bycatch. [PUBLICATION ABSTRACT] Incidental seabird mortality associated with bycatch during longline commercial fishing is a conservation concern. An initial step to estimating likelihood of seabird bycatch and conceiving conservation strategies is determining amount of overlap between foraging birds and commercial fishing effort, identifying oceanographic features associated with foraging birds, and quantifying dive characteristics. We tracked 24 adult flesh-footed shearwaters (Puffinus carneipes) breeding on Lord Howe Island located east of Australia during incubation and early and late chick-rearing periods from 6 January to 17 April 2005. At-sea foraging distribution of flesh-footed shearwaters was primarily confined within the jurisdictional Australian Fishing Zone. Foraging was strongly associated with sea-surface temperature >24° C. Spatial and temporal overlap of longline fishing with foraging shearwaters varied throughout the breeding season, but was greatest (63% overlap) during early chick-rearing. Mean maximum distance reached from the breeding colony during a foraging event was 804 km (SD = 280) from Lord Howe Island. Foraging behavior was strongly diurnal, with 91% of dives occurring during daylight, and most dives (77%) were <5 m. Given that longline fishing and flesh-footed shearwaters overlap substantially, the Australian Fisheries Management Authority should consider implementing additional regulations to further reduce bycatch. Conservation strategies such as setting longlines at nights may reduce flesh-footed shearwater bycatch. ABSTRACT Incidental seabird mortality associated with bycatch during longline commercial fishing is a conservation concern. An initial step to estimating likelihood of seabird bycatch and conceiving conservation strategies is determining amount of overlap between foraging birds and commercial fishing effort, identifying oceanographic features associated with foraging birds, and quantifying dive characteristics. We tracked 24 adult flesh‐footed shearwaters (Puffinus carneipes) breeding on Lord Howe Island located east of Australia during incubation and early and late chick‐rearing periods from 6 January to 17 April 2005. At‐sea foraging distribution of flesh‐footed shearwaters was primarily confined within the jurisdictional Australian Fishing Zone. Foraging was strongly associated with sea‐surface temperature >24°C. Spatial and temporal overlap of longline fishing with foraging shearwaters varied throughout the breeding season, but was greatest (63% overlap) during early chick‐rearing. Mean maximum distance reached from the breeding colony during a foraging event was 804 km (SD = 280) from Lord Howe Island. Foraging behavior was strongly diurnal, with 91% of dives occurring during daylight, and most dives (77%) were <5 m. Given that longline fishing and flesh‐footed shearwaters overlap substantially, the Australian Fisheries Management Authority should consider implementing additional regulations to further reduce bycatch. Conservation strategies such as setting longlines at nights may reduce flesh‐footed shearwater bycatch. ABSTRACT Incidental seabird mortality associated with bycatch during longline commercial fishing is a conservation concern. An initial step to estimating likelihood of seabird bycatch and conceiving conservation strategies is determining amount of overlap between foraging birds and commercial fishing effort, identifying oceanographic features associated with foraging birds, and quantifying dive characteristics. We tracked 24 adult flesh‐footed shearwaters ( Puffinus carneipes ) breeding on Lord Howe Island located east of Australia during incubation and early and late chick‐rearing periods from 6 January to 17 April 2005. At‐sea foraging distribution of flesh‐footed shearwaters was primarily confined within the jurisdictional Australian Fishing Zone. Foraging was strongly associated with sea‐surface temperature >24°C. Spatial and temporal overlap of longline fishing with foraging shearwaters varied throughout the breeding season, but was greatest (63% overlap) during early chick‐rearing. Mean maximum distance reached from the breeding colony during a foraging event was 804 km (SD = 280) from Lord Howe Island. Foraging behavior was strongly diurnal, with 91% of dives occurring during daylight, and most dives (77%) were <5 m. Given that longline fishing and flesh‐footed shearwaters overlap substantially, the Australian Fisheries Management Authority should consider implementing additional regulations to further reduce bycatch. Conservation strategies such as setting longlines at nights may reduce flesh‐footed shearwater bycatch. Incidental seabird mortality associated with bycatch during longline commercial fishing is a conservation concern. An initial step to estimating likelihood of seabird bycatch and conceiving conservation strategies is determining amount of overlap between foraging birds and commercial fishing effort, identifying oceanographic features associated with foraging birds, and quantifying dive characteristics. We tracked 24 adult flesh-footed shearwaters (Puffinus carneipes) breeding on Lord Howe Island located east of Australia during incubation and early and late chick-rearing periods from 6 January to 17 April 2005. At-sea foraging distribution of flesh-footed shearwaters was primarily confined within the jurisdictional Australian Fishing Zone. Foraging was strongly associated with sea-surface temperature >24 C. Spatial and temporal overlap of longline fishing with foraging shearwaters varied throughout the breeding season, but was greatest (63% overlap) during early chick-rearing. Mean maximum distance reached from the breeding colony during a foraging event was 804 km (SD = 280) from Lord Howe Island. Foraging behavior was strongly diurnal, with 91% of dives occurring during daylight, and most dives (77%) were <5 m. Given that longline fishing and flesh-footed shearwaters overlap substantially, the Australian Fisheries Management Authority should consider implementing additional regulations to further reduce bycatch. Conservation strategies such as setting longlines at nights may reduce flesh-footed shearwater bycatch. Incidental seabird mortality associated with bycatch during longline commercial fishing is a conservation concern. An initial step to estimating likelihood of seabird bycatch and conceiving conservation strategies is determining amount of overlap between foraging birds and commercial fishing effort, identifying oceanographic features associated with foraging birds, and quantifying dive characteristics. We tracked 24 adult flesh-footed shearwaters (Puffinus carneipes) breeding on Lord Howe Island located east of Australia during incubation and early and late chick-rearing periods from 6 January to 17 April 2005. At-sea foraging distribution of flesh-footed shearwaters was primarily confined within the jurisdictional Australian Fishing Zone. Foraging was strongly associated with sea-surface temperature >24°° C. Spatial and temporal overlap of longline fishing with foraging shearwaters varied throughout the breeding season, but was greatest (63%% overlap) during early chick-rearing. Mean maximum distance reached from the breeding colony during a foraging event was 804 km (SD == 280) from Lord Howe Island. Foraging behavior was strongly diurnal, with 91%% of dives occurring during daylight, and most dives (77%%) were <5 m. Given that longline fishing and flesh-footed shearwaters overlap substantially, the Australian Fisheries Management Authority should consider implementing additional regulations to further reduce bycatch. Conservation strategies such as setting longlines at nights may reduce flesh-footed shearwater bycatch. |
Author | Baker, G. Barry Thalmann, Sam J Tuck, Geoffrey N Hindell, Mark |
Author_xml | – sequence: 1 givenname: Sam J surname: Thalmann fullname: Thalmann, Sam J organization: Antarctic Wildlife Research Unit, School of Zoology, University of Tasmania, G.P.O. Box 252-05, Hobart, Tasmania 7001, Australia – sequence: 2 givenname: G. Barry surname: Baker fullname: Baker, G. Barry organization: Institute of Antarctic and Southern Ocean Studies, University of Tasmania, Private Bag 77, Hobart, Tasmania 7001, Australia – sequence: 3 givenname: Mark surname: Hindell fullname: Hindell, Mark organization: Antarctic Wildlife Research Unit, School of Zoology, University of Tasmania, G.P.O. Box 252-05, Hobart, Tasmania 7001, Australia – sequence: 4 givenname: Geoffrey N surname: Tuck fullname: Tuck, Geoffrey N organization: Australian Commonwealth Scientific and Industrial Research Organization Marine and Atmospheric Research, G.P.O. Box 1538, Hobart, Tasmania 7001, Australia |
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Decline in the distribution and abundance of flesh-footed shearwaters (Puffinus carneipes) on Lord Howe Island, Australia. Biological Conservation 128: 412-424. James, M. C., C. A. Ottensmeyer, and R. A. Myers. 2005. Identification of high-use habitat and threats to leatherback sea turtles on northern waters: new directions for conservation. Ecology Letters 8: 195-201. Warham, J. 1990. The petrels: their ecology and breeding systems. Academic Press, London, United Kingdom. Wood, K. A. 1990. Temporal and zonal patterns of abundance of shearwaters (Puffinus) off Central New South Wales. Australian Wildlife Research 17: 453-466. Lea, M.-A., C. Guinet, Y. Cherel, M. Hindell, L. Dubroca, and S. Thalmann. 2008. Colony-based foraging segregation by Antarctic fur seals at the Kerguelen Archipelago. Marine Ecology Progress Series 358: 273-287. Pitman, R. L. 1986. Seabird interactions with dolphins and tuna in the eastern tropical Pacific. Condor 88: 304-317. Spear, L. B., L. T. Ballance, and D. G. Ainley. 2001. Response of seabirds to thermal boundaries in the tropical Pacific: the thermocline versus the Equatorial Front. Marine Ecology Progress Series 219: 275-289. Brothers, N., R. Gales, A. Hedd, and G. Robertson. 1998. Foraging movements of the Shy Albatross Diomedea cauta breeding in Australia: implications for interactions with longline fisheries. Journal of Applied Ecology 140: 446-457. Alexander, K., G. Robertson, and R. Gales. 1997. The incidental mortality of albatrosses in longline fisheries. Australian Antarctic Division, Hobart, Tasmania, Australia. Hyrenbach, K. D., P. Fernandez, and D. J. Anderson. 2002. Oceanographic habitats of two sympatric North Pacific albatrosses during the breeding season. Marine Ecology Progress Series 233: 283-301. Polovina, J. J., E. Howell, D. R. Kobayashi, and M. P. Seki. 2001. The Transition Zone Chlorophyll Front, a dynamic global feature defining migration and forage habitat for marine resources. Progress in Oceanography 49: 469-483. Ballance, L. T., R. L. Pitman, and S. B. Reilly. 1997. Seabird community structure along a productivity gradient: importance of competition and energetic constraint. Ecology 78: 1502-1518. Berkman, P. A. 1992. The Antarctic marine ecosystem and humankind. Reviews in Aquatic Science 6: 295-333. Hunt, G. L., Jr.. 1991. Occurrence of polar seabirds at sea in relation to prey concentrations and oceanographic factors. Polar Research 10: 553-559. Hamer, K. C., and J. K. Hill. 1993. Variation and regulation of meal size and feeding frequency in Cory's shearwater Calonectris diomedea. Journal of Animal Ecology 62: 441-450. Andrews, J. C., M. W. Lawrence, and C. S. Nilsson. 1980. Observations of the Tasman Front. Journal of Physical Oceanography 10: 1854-1869. Teo, S. L. H., A. Boustany, S. Blackwell, A. Walli, K. C. Weng, and B. A. Block. 2004. Validation of geolocation estimates based on light level and sea surface temperature from electronic tags. Marine Ecology Progress Series 283: 81-98. Gudmundur, A. G., and T. Alerstam. 1998. Optimal map projections for analyzing long-distance migration routs. Journal of Avian Biology 29: 597-605. Phillips, R. A., J. R. D. Silk, J. P. Croxall, and V. Afanasyev. 2006. Year-round distribution of white-chinned petrels from South Georgia: relationships with oceanography and fisheries. Biological Conservation 192: 336-347. Worton, B. J. 1989. Kernel methods for estimating the utilization distribution in home-range studies. Ecology 70: 164-168. Nel, D. C., P. G. Ryan, and B. P. Watkins. 2002. Seabird mortality in the Patagonian toothfish longline fishery around the Prince Edward Islands, 1996-2000. Antarctic Science 14: 151-161. Shaffer, S. A., Y. Tremblay, J. A. Awkerman, R. W. Henry, S. L. H. Teo, D. J. Anderson, D. A. Croll, B. A. Block, and D. P. Costa. 2005. Comparison of light- and SST-based geolocation with satellite telemetry in free-ranging albatrosses. Marine Biology 147: 833-843. Department of Environment and Heritage. 2006. Threat Abatement Plan 2006 for the incidental catch (or bycatch) of seabirds during oceanic longline fishing operations. Prepared in consultation with the Longline Fishing TAP Team, Canberra, Australian Capital Territory, Australia. Warham, J. 1958. The nesting of the shearwater Puffinus carneipes. The Auk 75: 1-14. Hindell, M. A., H. R. Burton, and D. J. Slip. 1991. Foraging areas of southern elephant seals, Mirounga leonina, as inferred from water temperature data. Australian Journal of Marine and Freshwater Research 42: 115-128. Nel, D. C., J. R. E. Lutjeharms, E. A. Pakhomov, I. J. Ansorge, P. G. Ryan, and N. T. W. Klages. 2001. Exploitation of mesoscale oceano-graphic features by grey-headed albatross Thalassarche chrysostoma in the southern Indian Ocean. Marine Ecology Progress Series 217: 15-26. Inchausti, P., C. Guinet, M. Koudil, J. P. Durbec, C. Barbraud, H. Weimerskirch, Y. Cherel, and P. Jouventin. 2003. Inter-annual variability in the breeding performance of seabirds in relation to oceanographic anomalies that affect the Crozet and the Kerguelen sectors of the Southern Ocean. Journal of Avian Biology 34: 170-176. Tuck, G. N., T. Polacheck, J. P. Croxall, H. Weimerskirch, P. Prince, and S. Wotherspoon. 2001. The potential of archival tags to provide long-term movement and behaviour data for seabirds: first results from wandering albatross Diomedea exulans of South Georgia and the Crozet Islands. Emu 99: 60-68. Hindell, M. A., C. J. A. Bradshaw, M. D. Sumner, K. J. Michael, and H. R. Burton. 2003. Dispersal of female southern elephant seals and their prey consumption during the austral summer: relevance to management and oceanographic zones. Journal of Applied Ecology 40: 703-715. Ridgway, K. R., and J. R. Dunn. 2003. Mesoscale structure of the mean East Australian Current System and its relationship with topography. Progress in Oceanography 56: 189-222. BirdLife-International. 2004. Tracking ocean wanderers: the global distribution of albatrosses and petrels. Results from the Global Procellariform Tracking Workshop, 1-5 September 2003, Gordon's Bay, South Africa. Gilman, E., C. Boggs, and N. Brothers. 2003. Performance assessment of an underwater setting chute to mitigate seabird bycatch in the Hawaii pelagic longline tuna fishery. Ocean & Coastal Management 46: 985-1010. Packhomov, E. A., and C. D. McQuaid. 1996. Distribution of surface zooplankton and seabirds across the Southern Ocean. Polar Biology 16: 271-286. Rodhouse, P. G. 1996. Cephalopods and mesoscale oceanography at the Antarctic Polar Front: satellite tracked predators locate pelagic trophic interactions. Marine Ecology Progress Series 136: 37-50. Zar, J. 1999. Biostatistical analysis. Prentice Hall, Upper Saddle River, New Jersey, USA. Reid, T., and B. Sullivan. 2004. Longliners, black-browed albatross mortality and bait scavenging in Falkland Island waters: what is the relationship? Polar Biology 27: 131-139. Gould, P., P. Ostrom, and W. Walker. 1997. Food of flesh-footed shearwater Puffinus carneipes associated with high-seas driftnets in the central North Pacific Ocean. Emu 97: 168-173. Phillips, R. A., J. R. D. Silk, J. P. Croxall, V. Afanasyev, and D. R. Briggs 2002; 14 2002; 59 1997; 82 1993; 62 1991; 10 2004; 27 1990; 17 2004; 283 2002; 233 1999; 88 1999; 87 1999; 86 1971 2001; 49 1997; 3 1994; 63 2003; 56 1992; 6 1992; 8 2004; 31 2001 1990 1997; 97 1986; 88 2005; 147 1991; 42 1989; 70 2003; 46 2005; 305 2005; 74 1985 1988; 45 2008; 358 2001; 99 2001; 217 1996; 136 2003; 40 1998; 98 2006; 128 2001; 219 1998; 56 2004; 266 1998; 29 1993; 40 1998 1958; 75 1997 2000; 195 2006 1999; 21 1994 2006; 192 2004 2003 1996; 16 2003; 34 1999 2005; 126 2005; 8 1980; 10 1997; 78 2004; 13 1998; 140 Zar J. (e_1_2_1_70_1) 1999 e_1_2_1_60_1 e_1_2_1_20_1 e_1_2_1_41_1 e_1_2_1_68_1 Commonwealth of Australia (e_1_2_1_15_1) 2003 e_1_2_1_24_1 e_1_2_1_45_1 e_1_2_1_62_1 Nevitt G. (e_1_2_1_42_1) 1999 e_1_2_1_22_1 e_1_2_1_43_1 e_1_2_1_64_1 e_1_2_1_49_1 Prince P. A. (e_1_2_1_50_1) 1998 Department of Environment and Heritage (e_1_2_1_17_1) 2006 e_1_2_1_26_1 e_1_2_1_47_1 Alexander K. (e_1_2_1_2_1) 1997 Ashmole N. P. (e_1_2_1_4_1) 1971 Wood K. A. (e_1_2_1_66_1) 1993; 40 Brothers N. (e_1_2_1_11_1) 1998; 140 e_1_2_1_31_1 e_1_2_1_56_1 e_1_2_1_6_1 e_1_2_1_12_1 e_1_2_1_35_1 e_1_2_1_10_1 e_1_2_1_33_1 e_1_2_1_52_1 Caton A. E. (e_1_2_1_13_1) 2003 e_1_2_1_16_1 e_1_2_1_39_1 e_1_2_1_14_1 e_1_2_1_37_1 e_1_2_1_58_1 e_1_2_1_18_1 e_1_2_1_65_1 e_1_2_1_40_1 Rintoul S. R. (e_1_2_1_53_1) 2001 e_1_2_1_67_1 e_1_2_1_23_1 e_1_2_1_46_1 e_1_2_1_61_1 e_1_2_1_21_1 e_1_2_1_44_1 e_1_2_1_27_1 Hedd A. (e_1_2_1_28_1) 1997; 3 e_1_2_1_25_1 e_1_2_1_48_1 e_1_2_1_69_1 Berkman P. A. (e_1_2_1_8_1) 1992; 6 e_1_2_1_29_1 Warham J. (e_1_2_1_63_1) 1990 Roberston G. (e_1_2_1_54_1) 2001 e_1_2_1_7_1 e_1_2_1_30_1 e_1_2_1_55_1 e_1_2_1_5_1 e_1_2_1_57_1 e_1_2_1_3_1 BirdLife‐International (e_1_2_1_9_1) 2004 e_1_2_1_34_1 e_1_2_1_51_1 e_1_2_1_32_1 e_1_2_1_38_1 e_1_2_1_36_1 e_1_2_1_59_1 e_1_2_1_19_1 |
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Snippet | Incidental seabird mortality associated with bycatch during longline commercial fishing is a conservation concern. An initial step to estimating likelihood of... ABSTRACT Incidental seabird mortality associated with bycatch during longline commercial fishing is a conservation concern. An initial step to estimating... ABSTRACT Incidental seabird mortality associated with bycatch during longline commercial fishing is a conservation concern. An initial step to estimating... |
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SubjectTerms | animal behavior Aquatic birds Australia Australian Fishery Zone Birds Breeding Breeding seasons Bycatch Commercial fishing Environmental conservation Field study Fisheries Fisheries management Fishing zones flesh-footed shearwaters Foraging Foraging behavior geolocation habitat preferences habitat utilization longline fishery Longline fishing Management and Conservation Marine Marine ecology Marine mammals mortality Ocean fisheries Oceans Puffinus carneipes Sea birds Sea surface temperature seabird bycatch seabirds Temperature Tuna wildlife management |
Title | Longline Fisheries and Foraging Distribution of Flesh-Footed Shearwaters in Eastern Australia |
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