Anderson, Charles,Herrera, Miguel,Ilangakoon, Anoukchika,Koya, KM,Moazzam, M,Mustika, Putu L,Sutaria, Dipani N
Cetacean bycatch in Indian Ocean tuna gillnet fisheries Journal Article
In: Endangered Species Research, vol. 41, no. 292, pp. 39-53, 2020, ISSN: 1863-5407.
Abstract | Links | BibTeX | Tags: Bycatch, Estimates, Extrapolation, Gill net, gillnet, Indian Ocean, mortality, Observer programmes, Oman, Pakistan, Sri Lanka, Trends, tuna fishery
@article{,
title = {Cetacean bycatch in Indian Ocean tuna gillnet fisheries},
author = {Anderson, Charles,Herrera, Miguel,Ilangakoon, Anoukchika,Koya, KM,Moazzam, M,Mustika, Putu L,Sutaria, Dipani N},
url = {https://www.int-res.com/prepress/n01008.html},
doi = {https://doi.org/10.3354/esr01008},
issn = {1863-5407},
year = {2020},
date = {2020-01-01},
journal = {Endangered Species Research},
volume = {41},
number = {292},
pages = {39-53},
abstract = {Pelagic gillnet (driftnet) fisheries account for some 34% of Indian Ocean tuna catches. We combine published results from 10 bycatch sampling programmes (1981–2016) in Australia, Sri Lanka, India and Pakistan to estimate bycatch rates for cetaceans across all Indian Ocean tuna gillnet fisheries. Estimated cetacean bycatch peaked at almost 100,000 individuals yr–1 during 2004–2006, but has declined by over 15% since then, despite an increase in tuna gillnet fishing effort. These fisheries caught an estimated cumulative total of 4.1 million small cetaceans between 1950 and 2018. These bycatch estimates take little or no account of cetaceans caught by gillnet but not landed, of delayed mortality or sub-lethal impacts on cetaceans (especially whales) that escape from gillnets, of mortality associated with ghost nets, of harpoon catches made from gillnetters, nor of mortality from other tuna fisheries. Total cetacean mortality from Indian Ocean tuna fisheries may therefore be substantially higher than estimated here. Declining cetacean bycatch rates suggest that such levels of mortality are not sustainable. Indeed, mean small cetacean abundance may currently be 13% of pre-fishery levels. None of these estimates are precise, but they do demonstrate the likely order of magnitude of the issue. Countries with the largest current gillnet catches of tuna, and thus the ones likely to have the largest cetacean bycatch are (in order): Iran, Indonesia, India, Sri Lanka, Pakistan, Oman, Yemen, UAE and Tanzania. These 9 countries together may account for roughly 96% of all cetacean bycatch from tuna gillnet fisheries across the Indian Ocean. },
keywords = {Bycatch, Estimates, Extrapolation, Gill net, gillnet, Indian Ocean, mortality, Observer programmes, Oman, Pakistan, Sri Lanka, Trends, tuna fishery},
pubstate = {published},
tppubtype = {article}
}
Oman National Centre for Statistics; Information
Statistical Year Book Journal Article
In: vol. Issue 45, no. 390, pp. 447, 2017.
BibTeX | Tags: Arabian Sea, artisanal fisheries, commercial catch, dhow, Fisheries, Gill net, Oman, Sea of Oman
@article{,
title = {Statistical Year Book},
author = {Oman National Centre for Statistics and Information},
year = {2017},
date = {2017-01-01},
volume = {Issue 45},
number = {390},
pages = {447},
keywords = {Arabian Sea, artisanal fisheries, commercial catch, dhow, Fisheries, Gill net, Oman, Sea of Oman},
pubstate = {published},
tppubtype = {article}
}
Anderson, R Charles
Cetaceans and tuna fisheries in the Western and Central Indian Ocean Journal Article
In: International Pole and Line Federation Technical Report, vol. 2, no. 10, pp. 133, 2014.
Abstract | Links | BibTeX | Tags: Arabian Sea, Bycatch, cetaceans, Fisheries, Gill net, mitigation, Northern Indian Ocean, Regional management units, Tuna
@article{,
title = {Cetaceans and tuna fisheries in the Western and Central Indian Ocean},
author = {Anderson, R Charles},
url = {http://www.fao.org/3/a-bg252e.pdf},
year = {2014},
date = {2014-01-01},
journal = {International Pole and Line Federation Technical Report},
volume = {2},
number = {10},
pages = {133},
abstract = {This report reviews information on interactions between cetaceans (whales and
dolphins) and tuna fisheries in the western and central Indian Ocean. The average
annual catch of tuna and related species in the Indian Ocean was just over 1.5 million
tonnes during 2008-12. Of this, almost 1.1 million tonnes (71%) came from the
western and central Indian Ocean. The main fisheries for tuna and tuna-like species
in the region are gillnet (40% of reported catch during 2008-12), purse seine (26%),
longline (12%), handline and troll (11%) and pole-and-line (9%).
Major gillnet fishing nations include Iran, India, Sri Lanka, Pakistan, Oman and Yemen.
Cetacean bycatch must be large, but is poorly documented. A rough estimation,
based on the limited published information available, suggests that something
in excess of 60,000 small cetaceans might be taken as bycatch each year. There is
an urgent need for monitoring and management of these fisheries including the
development of mitigation methods to reduce cetacean bycatch. Large-scale gillnetting
on the high seas (using nets in excess of 2.5km length) is banned by both
UN convention and IOTC resolution, but is being carried out by Iran, Pakistan and
possibly also other countries; compliance is required. More generally, the large and
still expanding gillnet capacity within the region needs to be assessed, and if appropriate
either capped or reduced.
Purse seining in the western and central Indian Ocean is dominated by French and
Spanish fleets. An increasing proportion of sets is made on drifting fish aggregating
devices (FADs) but there has been, and continues to be, a considerable number of
sets made on free schools (i.e. non-FAD-associated tuna schools). Most cetaceans do
not regularly associate with FADs and the major potential cetacean interactions are
with free school sets. During 1981-1999, 9.6% of all sets were reported to have been
made in association with baleen whales, probably Bryde’s whales (Balaenoptera
brydei). When encircled, most whales are reported to escape by breaking through
the net. Mortality is unknown, but may have been of the order of 10s annually. The
association of free schools of large yellowfin tuna with dolphins (mostly spotted
dolphins Stenella attenuata and spinner dolphins Stenella longrostris) is more contentious.
This association (which is common in the Eastern Tropical Pacific and is
exploited by the purse seine fishery there) has always been reported to be rare in the
western Indian Ocean. However, the tuna-dolphin association is common in many
coastal areas of the region and widespread in the high seas of the western Indian
Ocean north of 10°S. Setting on dolphin schools has been also reported to be rare,
but its true scale is questioned. Setting on cetaceans has recently been banned by
EU regulation (2007) and IOTC resolution (2013), so cetacean bycatch and mortality
should be much reduced in the future. 100% coverage by international observers
would be ideal.
Longline fisheries were dominated for several decades by East Asian nations, but
now increasing catches are made by coastal countries, notably India, Sri Lanka and
Seychelles. A major issue for longliners is depredation – removal of bait and damage
of hooked fish by sharks and cetaceans. Several species of cetacean have been
implicated, but the main one appears to be the false killer whale (Pseudorca crassidens).
There is also some entanglement of cetaceans in longlines (likely following
attempts at depredation). Development of mitigation measures is on-going and
needs to be continued. It is possible that some longline fishermen are deliberately
killing cetaceans.
Several coastal countries have handline fisheries for large yellowfin tuna, which fishermen
locate by their association with dolphins (mainly spotted and spinner dolphins).
There is anecdotal evidence that some dolphins are hooked. Although they
invariably break free or are released, the scale of any post-release mortality or of
sub-lethal impacts is unknown. From the Maldivian pole-and-line fishery, there are
reports of dolphins (probably Indo-pacific bottlenose dolphins, Tursiops aduncus)
taking fish attracted by the lights used during night bait fishing. The scale and potential
impacts of these interactions require assessment.
There has been a widespread failure to monitor and manage cetacean bycatch in
Indian Ocean tuna fisheries, and to develop and implement mitigation measures.
The enormous, and still growing, gillnet capacity in the region should be of particular
concern. There is a need for increased observer coverage of all fisheries, supplemented
by electronic monitoring. Fishery-independent surveys of cetacean distribution
and abundance in the western Indian Ocean are also required to inform
management.},
keywords = {Arabian Sea, Bycatch, cetaceans, Fisheries, Gill net, mitigation, Northern Indian Ocean, Regional management units, Tuna},
pubstate = {published},
tppubtype = {article}
}
dolphins) and tuna fisheries in the western and central Indian Ocean. The average
annual catch of tuna and related species in the Indian Ocean was just over 1.5 million
tonnes during 2008-12. Of this, almost 1.1 million tonnes (71%) came from the
western and central Indian Ocean. The main fisheries for tuna and tuna-like species
in the region are gillnet (40% of reported catch during 2008-12), purse seine (26%),
longline (12%), handline and troll (11%) and pole-and-line (9%).
Major gillnet fishing nations include Iran, India, Sri Lanka, Pakistan, Oman and Yemen.
Cetacean bycatch must be large, but is poorly documented. A rough estimation,
based on the limited published information available, suggests that something
in excess of 60,000 small cetaceans might be taken as bycatch each year. There is
an urgent need for monitoring and management of these fisheries including the
development of mitigation methods to reduce cetacean bycatch. Large-scale gillnetting
on the high seas (using nets in excess of 2.5km length) is banned by both
UN convention and IOTC resolution, but is being carried out by Iran, Pakistan and
possibly also other countries; compliance is required. More generally, the large and
still expanding gillnet capacity within the region needs to be assessed, and if appropriate
either capped or reduced.
Purse seining in the western and central Indian Ocean is dominated by French and
Spanish fleets. An increasing proportion of sets is made on drifting fish aggregating
devices (FADs) but there has been, and continues to be, a considerable number of
sets made on free schools (i.e. non-FAD-associated tuna schools). Most cetaceans do
not regularly associate with FADs and the major potential cetacean interactions are
with free school sets. During 1981-1999, 9.6% of all sets were reported to have been
made in association with baleen whales, probably Bryde’s whales (Balaenoptera
brydei). When encircled, most whales are reported to escape by breaking through
the net. Mortality is unknown, but may have been of the order of 10s annually. The
association of free schools of large yellowfin tuna with dolphins (mostly spotted
dolphins Stenella attenuata and spinner dolphins Stenella longrostris) is more contentious.
This association (which is common in the Eastern Tropical Pacific and is
exploited by the purse seine fishery there) has always been reported to be rare in the
western Indian Ocean. However, the tuna-dolphin association is common in many
coastal areas of the region and widespread in the high seas of the western Indian
Ocean north of 10°S. Setting on dolphin schools has been also reported to be rare,
but its true scale is questioned. Setting on cetaceans has recently been banned by
EU regulation (2007) and IOTC resolution (2013), so cetacean bycatch and mortality
should be much reduced in the future. 100% coverage by international observers
would be ideal.
Longline fisheries were dominated for several decades by East Asian nations, but
now increasing catches are made by coastal countries, notably India, Sri Lanka and
Seychelles. A major issue for longliners is depredation – removal of bait and damage
of hooked fish by sharks and cetaceans. Several species of cetacean have been
implicated, but the main one appears to be the false killer whale (Pseudorca crassidens).
There is also some entanglement of cetaceans in longlines (likely following
attempts at depredation). Development of mitigation measures is on-going and
needs to be continued. It is possible that some longline fishermen are deliberately
killing cetaceans.
Several coastal countries have handline fisheries for large yellowfin tuna, which fishermen
locate by their association with dolphins (mainly spotted and spinner dolphins).
There is anecdotal evidence that some dolphins are hooked. Although they
invariably break free or are released, the scale of any post-release mortality or of
sub-lethal impacts is unknown. From the Maldivian pole-and-line fishery, there are
reports of dolphins (probably Indo-pacific bottlenose dolphins, Tursiops aduncus)
taking fish attracted by the lights used during night bait fishing. The scale and potential
impacts of these interactions require assessment.
There has been a widespread failure to monitor and manage cetacean bycatch in
Indian Ocean tuna fisheries, and to develop and implement mitigation measures.
The enormous, and still growing, gillnet capacity in the region should be of particular
concern. There is a need for increased observer coverage of all fisheries, supplemented
by electronic monitoring. Fishery-independent surveys of cetacean distribution
and abundance in the western Indian Ocean are also required to inform
management.