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| Location | Gear | Catch | Technique | Bycatch species | Type | Results |
|---|---|---|---|---|---|---|
western North Pacific Ocean (Japan) |
Hooks and Lines
|
Not specified |
Circle hooks
|
Elasmobranchs, Sharks, Prionace glauca (Blue shark) | Field study in the wild | The use of circle hooks (4.3 sun and 5.2 sun) instead of standard Japanese tuna hooks (3.8 sun) in the pelagic longline fishery in the western North Pacific, had little impact on catch rates, mortality or size composition of blue sharks (Prionace glauca). Circle hooks did not impact the catch rates, mortality or size composition of blue sharks |
western Pacific Ocean |
Hooks and Lines
|
Southern bluefin tuna (Thunnus maccoyii) |
Visual deterrents
|
Seabirds | Field study in the wild | Four parts of the tori-pole were tested for their effectiveness in reducing the incidental catch of albatross in the Japanese southern bluefin tuna (Thunnus maccoyii) longline fishery. Observer data were used to test: 1. bird line material, 2. streamer material, 3. bird line length and 4. pole height above sea surface. The effectiveness of tori-poles in reducing albatross interactions increased with a longer bird line, but there was no difference in the effectiveness between the different bird line materials, type of streamer material or pole height above the sea surface. The effectiveness of tori-poles in reducing albatross interactions increased with a longer bird line, but there was no difference in the effectiveness between the different bird line materials, type of streamer material or pole height above the sea surfac |
Cape May, New Jersey, United States |
Traps
|
Blue crab (Callinectes sapidus) |
Excluder devices
|
Terrapins, Malaclemys terrapin (Diamondback terrapin) | Field study in the wild | Several versions of a terrapin excluder design were tested on crab traps to determine how effective they were in reducing northern diamondback terrapin (Malaclemys terrapin) bycatch, as well as the effect on catch rates of targeted blue crabs (Callinectes sapidus). All tests consisted of modified and unmodified traps being set in an alternate fashion. A wire bar placed across the opening of the traps was unsuccessful in reducing terrapin bycatch. A second design, which was a rectangular frame (5x10 cm) was successful. Standard traps caught 13 out of 15 terrapins during 1992 and 46 out of 51 during 1995, with the remainder of terrapins being caught by traps modified with the frame. Additional testing of the rectangular frame size, determined the 4.5x10 cm frame reduced terrapin bycatch the most (22 terrapins caught in unmodified vs. none in modified traps). Additionally, crab catch rates were 9% higher in the modified traps (4.5x10 cm) compared to the unmodified traps and crabs were of similar sizes in the two traps. In comparison, crab catch rates were 11% higher than in the unmodified traps when the 5x10 cm excluder design was used in 1994 (multiple sites) and 49% higher in 1995 (single site). Standard traps caught 13 out of 15 terrapins during 1992 and 46 out of 51 during 1995, with the remainder of terrapins being caught by traps modified with the frame. Additional testing of the rectangular frame size, determined the 4.5x10 cm frame reduced |
N/A |
N/A | Seabirds, Diomedea antipodensis (Antipodean albatross) | Summary study | Interaction risk between the endangered Antipodean albatross (Diomedea antipodensis antipodensis) and fisheries was assessed by combining satellite-tracking data of individuals with data from AIS vessel tracking, as well as oceanographic data to determine how physical ocean features shape high-risk interaction zones. Hotspots for interactions ranged from 25°S to 40° S, varied seasonally, and were significantly higher in May-August and among juveniles. Interaction risk was also greatest where thermal fronts occur. Regional Fisheries Management Organizations could extend current bycatch mitigation measures to include fishing groups between 25 and 30°S to cover seasonal hotspots for juvenile and females. |
||
British Columbia, Canada |
Gillnets and Entangling Nets
|
Salmon | Small Cetaceans (maximum length < 7.5 meters), Lagenorhynchus obliquidens (Pacific white-sided dolphin), Phocoenoides dalli (Dall's porpoise), Phocoena phocoena (Harbor porpoise) | Field study in the wild | 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. The researchers 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 favorable conservation status of cetacean populations. |
|
| Field study in the wild | Mobulid rays are distributed worldwide in tropical and warm temperate waters, and are landed as bycatch in many different fisheries. Five mobulid species (Mobula birostris, M. japanica, M.munkiana, M. tarapacana and M.thurstoni) are currently listed as vulnerable by the IUCN Red List for Threatened Animals for at least part of their geographic distribution. There is a lack of information on mobulid populations, and consequently it is very difficult to determine how the level of exploitation of mobulids in Indonesia may affected their stocks. Data in this study were derived from 409 mobulids that were taken as bycatch in drift gillnet fisheries targeting skipjack tuna (Katsuwonus pelamis), and subsequently examined at fish landing sites in Indonesia. Results identified M. japanica and M. tarapacana as the most abundant species represented. The disc width at maturity (DW50) of males, derived from the proportion of males at each size class with fully calcified claspers, ranged from 1538 mm for M. thurstoni to 3752 mm for M. birostris. The very low fecundity of the large and probably long-lived mobulid rays make the stocks of their species particularly susceptible to further increases in fishing. |