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Displaying 31 - 40 of 92
Location Gear Catch Technique Bycatch species Type Results

Western Australia

Trawls
red emperor, scarlet perch, spangled emperor, Rankin cod, blue spot emperor, rosy threadfin brea, flagfish, frypan snapper, red snapper and goldband snapper
Excluder devices
Small Cetaceans (maximum length < 7.5 meters) Field study in the wild
Summary: A semi-flexible exclusion grid with a bar spacing of 15.5 cm reduced dolphin bycatch in the Pilbara trawl fishery by close to 50% and reduced the bycatch of sea turtles, large sharks and rays. However, the fate of the dolphins that encountered the grid and escaped is unknown.
Effect on Bycatch: Reduced dolphin bycatch by almost 50% and reduced bycatch of sea turtles, large sharks and large rays
Reference:
Stephenson, P.C., Wells, S., King, J.A., 2008 , Evaluation of exclusion grids to reduce the bycatch of dolphins, turtles, sharks and rays in the Pilbara trawl fishery

Akaroa Harbour, New Zealand

Gillnets and Entangling Nets
None reported
Acoustic deterrent devices
Small Cetaceans (maximum length < 7.5 meters) Field study in the wild
Summary:

White Dukane pingers with a fundamental frequency of 10kHz and harmonies of up to 160 kHz, elicited the strongest response from Hector's dolphins, compared to the black Pice and red Dukane pingers. More than half (62.5%) of the dolphins exhibited avoidance when exposed to the white pinger. However, no significant differences between pingers were found in the rate of echolocation clicks per dolphin or dolphin group, or among the peak frequencies of subset clicks.

Effect on Bycatch: 62.5% of individuals elicited avoidance behavior (using white Dukane pingers)
Reference:
Stone, G.S., Cavagnaro, L., Hutt, A., Kraus, S., Baldwin, K., Brown, J., 2000 , Reactions of Hector's dolphins to acoustic gillnet pingers

North Sea

Gillnets and Entangling Nets
Cod
Acoustic deterrent devices
Small Cetaceans (maximum length < 7.5 meters), Phocoena phocoena (Harbor porpoise) Field study in the wild
Summary: Gillnets from the North Sea wreck net fishery equipped with pingers, had a 100% reduction in the bycatch of harbour porpoises, compared to nets with no pingers attached.
Effect on Bycatch: 100% reduction in harbor porpoise bycatch
Reference:
Larsen, F., Vinther, M., Krog, C. , 2002 , Use of pingers in the Danish North Sea wreck net fishery

North Sea

Gillnets and Entangling Nets
Cod
Acoustic deterrent devices
Small Cetaceans (maximum length < 7.5 meters), Phocoena phocoena (Harbor porpoise) Field study in the wild
Summary:

Bottom set gillnets with pingers (LU-1, 8 signals, 145 dB, 300 ms, random signal intervals) attached were tested against standard nets and nets with dummy pingers (double blind) to determine if they could reduce the incidental capture of harbour porpoises. The proportion (number of nets with porpoises/number without) of harbour porpoise bycatch was reduced from 0.00229 and 0.00295 for nets with dummy pingers and no pingers respectively, to 0.00015 for nets with active pingers. The difference in bycatch rates between nets with active and dummy pingers was statistically significant but not between nets with dummy pingers and with no pingers.

Effect on Bycatch: Reduced catch rates from 0.00229 and 0.00295 for nets with dummy pingers and no pingers respectively, to 0.00015 for nets with active pingers
Reference:
Larsen, F., 1999 , The effect of acoustic alarms on the by-catch of harbour porpoises in the Danish North Sea gill net fishery

British Columbia, Canada

Gillnets and Entangling Nets
Salmon Small Cetaceans (maximum length < 7.5 meters), Phocoena phocoena (Harbor porpoise) Summary study
Summary:

Small cetaceans are by-caught in salmon gillnet fisheries in British Columbia (BC) waters. In Canada, there is currently no generic calculation to identify when management action is necessary to reduce cetacean bycatch below sustainable limits. We estimated potential anthropogenic mortality limits for harbour (Phocoena phocoena) and Dall’s (Phocoenoides dalli) porpoises and Pacific white-sided dolphins (Lagenorhynchus obliquidens) using quantitative objectives from two well-established frameworks for conservation and management (the United States’ Marine Mammal Protection Act and the Agreement on the Conservation of Small Cetaceans of the Baltic and North Seas), which are similar to some management objectives developed for marine mammal stocks elsewhere in Canada. Limits were calculated as functions of (i) a minimum abundance estimate (2004–2005); (ii) maximum rate of population increase; and (iii) uncertainty factors to account for bias in abundance estimates and uncertainty in mortality estimates. Best estimates of bycatch mortality in 2004 and 2005 exceeded only the most precautionary limits and only for porpoise species. Future research priority should be given to determining small cetacean stock structure in BC and refining species-specific entanglement rates in these and other fisheries. The approach offers a quantitative framework for Canada to meet its stated objectives to maintain favourable conservation status of cetacean populations.

Reference:
Williams, R., Hall, A., Winship, A., 2008 , Potential limits to anthropogenic mortality of small cetaceans in coastal waters of British Columbia

Baltic

Gillnets and Entangling Nets
None reported
Acoustic deterrent devices
Small Cetaceans (maximum length < 7.5 meters), Phocoena phocoena (Harbor porpoise) Field study in the wild
Summary: Authors investigated the spatial and temporal responses of porpoises to simulated bottom-set nets equipped with periodically operating Dukane NetMark 1000 pingers.
Effect on Bycatch: Pingers significantly reduced echolocation encounter rates by 50-100% at 500m; sighting reduced up to 375m. Porpoise return time was 6 hrs when pingers were silent after being active for 24 hrs 50 min
Reference:
Carlstrom J., Berggren P., Tregenza N.J.C, 2009 , Spatial and temporal impact of pingers on porpoises

Sardinia, Italy

fin-fish farm
Acoustic deterrent devices
Small Cetaceans (maximum length < 7.5 meters) Field study in the wild
Summary:

Acoustic harassment devices (AHDs) were tested in association with a marine fin-fish farm off the north-eastern coast of Sardinia, to determine their effectiveness on common bottlenose dolphins.  This was a controlled exposure experiment.  No significant or immediate effects on bottlenose dolphin presence, distance from AHD, group size or time spent in the fish farm area were caused by activation of the AHD. Thus, additional research is needed on their effectiveness in the marine environment before further deployment.

Effect on Bycatch: No significant effect on bottlenose dolphins' presence, distance from AHD, group size or time spent in the fish farm area

Seychelles

Hooks and Lines
Tunas and swordfish
Net sleeves
Small Cetaceans (maximum length < 7.5 meters) Field study in the wild
Summary:

Two types of depredation mitigation devices (DMD) were designed and tested aboard pelagic longline fishing vessels targeting tunas and swordfish off the Seychelles.  The DMD's were designed to reduce the damage and removal of fish from the fishing gear by predators such as toothed whales and sharks. The first DMD was termed "spider" and was made up of a 100 mm diameter plastic disc with sixteen holes in its outer range and a 37 mm diameter central hole.  Eight 1200 mm long hanging legs were created by placing four polyester strands into the outer holes and the entire system is triggered by a biting fish.  The second DMD, "sock", was designed to cover the fish to hide it from predators through either a net made up of fiberglass mosquito netting or of propylene fiber net.  Shark depredation was significantly higher throughout the surveys than toothed whale depredation, but toothed whales caused more damaged to fish through depredation events. The sock DMD did not affect the catch rates of targeted species or depredation events by either sharks or toothed whales.  These results for the spider DMD were not presented. Trigger rates for the two DMD's were up to 87.3% for the spider and 69.2% for the sock.  The protection rate was as high as 80% for spider but only 15.5% for the sock. Entanglement rates of the DMD's with the fishing gear were low for the spider (3.6%) and higher for the sock (17.8%).  In addition, the use of these DMD's signficantly slowed down the fishing process, and therefore additional work into the design and application of DMD's needs to be explored.

Effect on Bycatch: Sock DMD did not affect depredation. Shark depredation was higher
Reference:
Rabeariosa, N., Bach, P., Tixier, P. and Guinet, C., 2012 , Pelagic longline fishing trials to shape a mitigation device of the depredation by toothed whales

Southwest England

Gillnets and Entangling Nets
None reported
Acoustic deterrent devices
Small Cetaceans (maximum length < 7.5 meters), Phocoena phocoena (Harbor porpoise) Field study in the wild
Summary:

Fisheries observers and skippers tested the effectiveness of the Dolphin Dissuasive Device (DDD) as a bycatch mitigation tool for porpoises and dolphins. This study was conducted aboard fishing vessels in the Cornish over-12m static net sector fishery in the waters of Southwest England. DDD's were placed at the end nets. The DDD's caught significantly fewer porpoises but no significant difference in dolphin bycatch was observed. When bycatch rates were separated between short (up to 4 km) fleets and long (larger than 4 km) fleets, there was no significant difference in porpoise bycatch in the long fleet but there was in the short fleet. 

Effect on Bycatch: DDD's caught significantly fewer porpoises but no significant difference in dolphin bycatch was observed
Reference:
Kingston, A. and Northridge, S., 2011 , Extension trial of an acoustic deterrent system to minimize dolphin and porpoise bycatch in gill and tangle net fisheries

Cornwall

Gillnets and Entangling Nets
Monkfish
Acoustic deterrent devices
Small Cetaceans (maximum length < 7.5 meters), Phocoena phocoena (Harbor porpoise) Field study in the wild
Summary:

Tests were conducted aboard small (<10 m long) static net fishing vessels targeting monkfish off the coast of Britain to determine the response of cetaceans to pingers.  AQUAmark 100 pingers were positioned at 200 m intervals on the net and acoustic click detectors (C-PODs) were placed at the end of 1 km tiers of the net to determine the response of cetaceans to the pingers.  Only one harbour porpoise was incidentally caught during these trials and there was a significant reduction in the number of porpoise clicks recorded at nets with pingers compared to those without.  Additional tests were conducted to determine habituation.  For these tests, modified pingers, active for alternate seven hour periods, were attached below click detectors at one site with strong tides and loud ambient noise and one at a quite site.  The results of this part of the study showed the pinger effect was stronger at the quiet site and that were was no habituation.  In addition, there was evidence of exclusion of porpoises following pinger use for as much as seven hours.

Effect on Bycatch: One incidentally caught harbor porpoise; significant reduction in the number of porpoise clicks at nets with pingers. Pinger effects stronger at quiet sites; no habituation observed, exclusion of porpoises following pinger use for as much as 7 hrs
Reference:
Hardy, T., Williams, R., Caslake, R. and Tregenza, N., 2012 , An investigation of acoustic deterrent devices to reduce cetacean bycatch in an inshore set net fishery

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