Search The Database
| Location | Gear | Catch | Technique | Bycatch species | Type | Results |
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Sub-surface sets (gillnets)
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Small Cetaceans (maximum length < 7.5 meters) | Summary study | In the Indian Ocean tuna gillnet fisheries, cetacean bycatch is very high, but it is understudied and poorly understood. This paper investigates the issue and makes specific recommendations to strengthen knowledge and management: improve catch and bycatch reporting, increase research and analyses of cetaceans in the region in order to assess bycatch, revise the conservation measure adopted to address the bycatch of cetaceans in IOTC fisheries (Resolution 23/06) to include additional reporting for gillnets operating in EEZs, and expand the use of mitigation methods, such as setting gillnets 2m below the surface.
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Bay of Biscay |
Trawls
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bony fishes: hake, blue whiting, mackerel |
Acoustic deterrent devices
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Small Cetaceans (maximum length < 7.5 meters) | Field study in the wild | The authors evaluated the effectiveness of DDD®03H Dolphin Dissuasive Devices, or DDD pingers (an acoustic deterrent device) to reduce common dolphin (Delphinus delphis) bycatch in a demersal pair trawler in the Bay of Biscay. Results showed that the DDD pingers reduced common dolphin bycatch by more than 90%, and that common dolphin bycatch in this trawl fishery is related to fishing zone and depth, but not necessarily factors such as time of day and haul duration.
significantly reduced bycatch of common dolphin, both by frequency and # of individuals per haul |
Peru |
Gillnets and Entangling Nets
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unspecified | Small Cetaceans (maximum length < 7.5 meters) | Field study in the wild | The authors performed onboard surveys (line transects and passive acoustic monitoring) and interviewed gillnet fishers to assess abundance and bycatch of the endemic Burmeister’s porpoises (Phocoena spinipinnis) in northern Peru in 2023. The population abundance in the study area was estimated at 1,696 spatially distributed individuals, with the highest densities found within 25km of shore and within shallow waters ≤50 m. Fishers' descriptions of bycatch aligned with survey results, and most fishers reported experiencing porpoise bycatch the previous year. The annual bycatch rate was estimated to be 420 porpoises across the entire artisanal gillnet fishery of Salaverry, which far exceeds sustainable limits and highlights the urgent need for bycatch mitigation measures.
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Iceland |
Gillnets and Entangling Nets
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Atlantic cod (Gadus morhua) |
Acoustic deterrent devices
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Small Cetaceans (maximum length < 7.5 meters), Phocoena phocoena (Harbor porpoise) | Field study in the wild | Three types of acoustic deterrent devices were tested in the Icelandic cod gillnet fishery: Fishtek Banana pingers, Porpoise ALert devices (PAL), and wideband PAL (wPAL) with a modified pinger signal (PAL device emitting a wideband pinger signal with a frequency range of 20 – 160 kHz and signal duration of 0.3 s (every 4–30 s) with the same source level at 145 db and maximum depth (320 m)). Banana pingers and PALs did not demonstrate any reduction of bycatch of marine mammals, while the wPAL-equipped nets had no bycatch during the trial. Fish catch and overall commercial value was significantly reduced in gillnets equipped with banana pingers and PALs. Use of banana pingers and porpoise alert devices (PALs) had roughly the same rates of bycatch as the control, while wideband PALs did not record any marine mammal bycatch (control = 14 marine mammals). |
Karachi, Pakistan |
Gillnets and Entangling Nets
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Tuna spp. |
Sub-surface sets (gillnets)
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Small Cetaceans (maximum length < 7.5 meters), Sea Turtles | Field study in the wild | The study examined individual and cumulative bycatch during the first five years of a fisher engagement program in the tuna drift gillnet fishery in Pakistan, where fishers co-developed a sub-surface net setting strategy while also receiving bycatch awareness and safe release training. Captain identity and year were the strongest predictors of sea turtle and dolphin bycatch rates. 95% reduction in cumulative dolphin bycatch over four years; 90% reduction in cumulative sea turtle bycatch |
Western Baltic Sea (ICES SD22) |
Gillnets and Entangling Nets
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plaice (Pleuronectes platessa), flounder (Platichthys flesus), dab (Limanda limanda) and turbot (Scophthalmus maximus) |
Acoustic deterrent devices
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Large Cetaceans (maximum length > 7.5 meters), Small Cetaceans (maximum length < 7.5 meters) | Field study in the wild | The PearlNet aims to mitigate odontocete bycatch in bottom-set gillnets by enhancing the acoustic visibility of nets through the incorporation of small, acrylic glass spheres. This study found that PearlNet performed similarly to standard nets in terms of catch efficiency and handling time of gear. Performance of the gear in reducing marine mammal bycatch was not assessed during this study, however, no mammal bycatch was reported. Not tested (but none observed during study) |
Black Sea, Bulgaria |
Gillnets and Entangling Nets
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Turbot (Scophthalmus maximus) |
Acoustic deterrent devices
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Small Cetaceans (maximum length < 7.5 meters), Phocoena phocoena (Harbor porpoise) | Field study in the wild | Between 2019 and 2022, trials using three different pinger models (Future Oceans 10 kHz, Future Oceans 70 kHz, and PAL Wideband) were conducted in Bulgaria during standard turbot fishing operations. Marine mammal bycatch was observed in 61% of all hauls. No significant difference in bycatch rates between active and control nets was observed in trials involving Future Oceans 10 kHz (17 trials) and 70 kHz (6 trials) pingers. However, a significant reduction (74%) in cetacean bycatch was recorded during the trials conducted with PAL Wideband pingers. Future Oceans 10kHz and Future Oceans 70kHz pingers did not significantly impact bycatch; PAL Wideband resulted in a 74% reduction in cetacean bycatch |
Menai Bay, Zanzibar, Tanzania |
Gillnets and Entangling Nets
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Large pelagic finfish (primarily Euthynnus affinis, Katsuwonus pelamis, Istiophorus platypterus, Makaira indica, Xiphias gladius, and Scomberomorus commerson) |
Acoustic deterrent devices
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Small Cetaceans (maximum length < 7.5 meters), Tursiops aduncus (Indo-Pacific bottlenose dolphin) | Field study in the wild | The study tested the use of glass and plastic drink bottles as low-cost bycatch mitigation devices (mechanical pingers and acoustic reflectors, respectively) in gillnet fisheries across three regions/fisheries: surface-set driftnet fisheries in Zanzibar and Peru and bottom-set trammel net fisheries in Brazil. In Brazil, plastic bottles reduced dolphin bycatch while increasing fish catch, although further trials are needed. In Peru, glass bottles had no effect on dolphin, porpoise, or turtle bycatch but altered target elasmobranch and teleost catches; plastic bottles similarly had no effect on dolphin bycatch but increased shark catch. In Zanzibar, no dolphin bycatch was recorded in any sets, though plastic bottles increased tuna catch. |
Salaverry, Peru |
Gillnets and Entangling Nets
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Elasmobranchs, dolphinfish (Coryphaena sp.), billfish (Xiphias sp.), and bonito (Sarda sp.) |
Acoustic deterrent devices
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Small Cetaceans (maximum length < 7.5 meters), Lagenorhynchus obscurus (Dusky dolphin), Phocoena spinipinnis (Burmeister's porpoise), Tursiops truncatus (Bottlenose dolphin) | Field study in the wild | The study tested the use of glass and plastic drink bottles as low-cost bycatch mitigation devices (mechanical pingers and acoustic reflectors, respectively) in gillnet fisheries across three regions/fisheries: surface-set driftnet fisheries in Zanzibar and Peru and bottom-set trammel net fisheries in Brazil. In Brazil, plastic bottles reduced dolphin bycatch while increasing fish catch, although further trials are needed. In Peru, glass bottles had no effect on dolphin, porpoise, or turtle bycatch but altered target elasmobranch and teleost catches; plastic bottles similarly had no effect on dolphin bycatch but increased shark catch. In Zanzibar, no dolphin bycatch was recorded in any sets, though plastic bottles increased tuna catch. No significant difference between control and glass and control and plastic bottles |
Torres and Passo de Torres, Brazil |
Gillnets and Entangling Nets
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Brazilian flounder (Paralichtys spp.) and whitemouth croaker (Micropogonias furnieri) |
Acoustic deterrent devices
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Small Cetaceans (maximum length < 7.5 meters), Tursiops truncatus (Bottlenose dolphin), Pontoporia blainvillei (Franciscana dolphin) | Field study in the wild | The study tested the use of glass and plastic drink bottles as low-cost bycatch mitigation devices (mechanical pingers and acoustic reflectors, respectively) in gillnet fisheries across three regions/fisheries: surface-set driftnet fisheries in Zanzibar and Peru and bottom-set trammel net fisheries in Brazil. In Brazil, plastic bottles reduced dolphin bycatch while increasing fish catch, although further trials are needed. In Peru, glass bottles had no effect on dolphin, porpoise, or turtle bycatch but altered target elasmobranch and teleost catches; plastic bottles similarly had no effect on dolphin bycatch but increased shark catch. In Zanzibar, no dolphin bycatch was recorded in any sets, though plastic bottles increased tuna catch. No dolphins caught as bycatch in sets using plastic bottles, compared to four in the control (sample size too small to generate significance) |