32 research outputs found
Bycatch and strandings programs as ecological indicators for data-limited cetaceans
An integrated approach of using strandings and bycatch data may provide an indicator of long-term trends for data-limited cetaceans. Strandings programs can give a faithful representation of the species composition of cetacean assemblages, while standardised bycatch rates can provide a measure of relative abundance. Comparing the two datasets may also facilitate managing impacts by understanding which species, sex or sizes are the most vulnerable to interactions with fisheries gear. Here we apply this approach to two long-term datasets in East Australia, bycatch in the Queensland Shark Control Program QSCP, 1992–2012) and strandings in the Queensland Marine Wildlife Strandings and Mortality Program StrandNet, 1996–2012). Short-beaked common dolphins, Delphinus delphis, were markedly more frequent in bycatch than in the strandings dataset, suggesting that they are more prone to being incidentally caught than other cetacean species in the region. The reverse was true for humpback whales, Megaptera novaeangliae, bottlenose dolphins, Tursiops spp.; and species predominantly found in offshore waters.
QSCP bycatch was strongly skewed towards females for short-beaked common dolphins, and towards smaller sizes for Australian humpback dolphins, Sousa sahulensis. Overall, both datasets demonstrated similar seasonality and a similar long-term increase from 1996 until 2008. Analysis on a species-by-species basis was then used to explore potential explanations for long-term trends, which ranged from a recovering stock (humpback whales) to a shift in habitat use (short-beaked common dolphins)
Ghost fishing in the pot fishery for blue swimmer crabs Portunus pelagicus in Queensland, Australia
Blue swimmer crabs (Portunus pelagicus) are an economically important crab caught in baited traps throughout the Indo-west Pacific and Mediterranean. In Australia they are traditionally caught using rigid wire traps (approximate to pots) but there has been a recent increase in the use of collapsible pots constructed from polyethylene trawl mesh. Two experiments were conducted in Moreton Bay, Queensland, to determine the ghost fishing potential of lost crab pots on both target and bycatch species and to evaluate the differences between traditional and contemporary pot designs. A lost contemporary, collapsible trawl mesh pot will catch between 3 and 223 R pelagicus per year after the bait has been exhausted, while a traditional wire mesh pot would catch 11-74 crabs peryear. As most fishers now use the collapsible trawl mesh pots, ghost fishing mortality could be as high as 111,811-670,866 crabs per year. Bycatch retention was also higher in contemporary designs. Periods of strong winds appeared to increase the ghost fishing potential of lost pots. The use of escape gaps, larger mesh sizes and construction options that allow for the deterioration of entrance funnels to minimise ghost fishing are recommended to reduce environmental impacts
Surviving the effects of barotrauma: assessing treatment options and a ‘natural’ remedy to enhance the release survival of line caught pink snapper (Pagrus auratus)
A new technique to ameliorate the effects of barotrauma was tested based on observations of pink snapper, Pagrus auratus (Forster), inadvertently piercing their everted stomach with their teeth and releasing trapped swim bladder gases. This technique was termed buccal venting and involved piercing the everted stomach protruding into the buccal cavity or out of the mouth with a 16-gauge hypodermic needle (a practice previously not encouraged). Short-term (~3 days) survival of buccal-vented fish was not significantly different from laterally vented fish nor untreated controls. Both buccal and lateral venting techniques were shown to cause no harm and allowed fish to return to depth. The short-term (1–3 days) post-release survival of line caught snapper was 88% with no significant difference in survival across three depth ranges tested (37–50, 51–100 and 101–180 m). Survival of sublegal pink snapper ( 0.05) from that of legal-sized fish (≥35 cm TL). Healing of the swim bladder was observed in 27% of pink snapper dissected after ≤3 days in captivity, and healing of stomachs was observed in 64% of pink snapper that had been buccal vented. Relatively high post-release survival rates of line caught pink snapper may offer some protection for snapper stocks where high fishing pressure and legal size restrictions result in the majority of the catch having to be released
Short-term survival of discarded pearl perch (Glaucosoma scapulare Ramsay, 1881) caught by hook-and-line in Queensland, Australia
Post-release survival of line-caught pearl perch (Glaucosoma scapulare) was assessed via field experiments where fish were angled using methods similar to those used by commercial, recreational and charter fishers. One hundred and eighty-three individuals were caught during four experiments, of which >91% survived up to three days post-capture. Hook location was found to be the best predictor of survival, with the survival of throat- or stomach-hooked pearl perch significantly (P < 0.05) lower than those hooked in either the mouth or lip. Post-release survival was similar for both legal (≥35 cm) and sub-legal (<35 cm) pearl perch, while those individuals showing no signs of barotrauma were more likely to survive in the short term. Examination of the swim bladders in the laboratory, combined with observations in the field, revealed that swim bladders rupture during ascent from depth allowing swim bladder gases to escape into the gut cavity. As angled fish approach the surface, the alimentary tract ruptures near the anus allowing swim bladder gases to escape the gut cavity. As a result, very few pearl perch exhibit barotrauma symptoms and no barotrauma mitigation strategies were recommended. The results of this study show that pearl perch are relatively resilient to catch-and-release suggesting that post-release mortality would not contribute significantly to total fishing mortality. We recommend the use of circle hooks, fished actively on tight lines, combined with minimal handling in order to maximise the post-release survival of pearl perch
Development of non-damaging trapping apparatus and methods of limiting damage caused by traditional tangle nets in the spanner crab (Ranina ranina) fishery
Both male and female spanner crabs (Ranina ranina) readily moved up inclined ramps made from numerous materials and there were no significant size related behavioral differences. This suggested that Ranina ranina could be trapped in "entrance type" non-entangling apparatus. A range of top and side entrance traps as well as conventional entanglement nets were trialed in the laboratory with entanglement nets entrapping over double the number of crabs caught in the most efficient non-entanglement trap tested. This was largely due to the greater time required by spanner crabs to find the entrance of a trap. Field trials supported the laboratory behavioural observations with no trap obtaining comparable catches to the conventional entangling apparatus. When fishing times of non-entangling traps were increased, catch rates likewise increased however the logistics and cost-effectiveness of their commercial use proved prohibitive.
Field trails using different configurations of mesh size, numbers of mesh layers, ply and net tension for conventional entangling apparatus were also conducted to identify the most efficient net configuration for minimising damage whilst maintaining catch rates. Both small (25 mm) and large (85 mm) mesh size required more time to clear than intermediate sizes. Likewise dactyl loss was higher for these meshes, particularly the 25 mm mesh. Loosely hung nets induced over double the dactyl loss of tightly hung nets, with longer clearance time. In addition the catch of undersize crabs was also significantly greater in loosely hung nets whilst there was no significant difference in the catch of legal sized crabs. Tightly hung single mesh nets of a mesh size greater than 25 mm and less than 85 mm proved to be the most effective net for minimizing damage whilst maintaining catch rates
Biological data and model development for management of longfinned eels
Objectives:
1. Estimate population parameters required for a management model. These include survival, density, age structure, growth, age and size at maturity and at recruitment to the adult eel fishery. Estimate their variability among individuals in a range of habitats.
2. Develop a management population dynamics model and use it to investigate management options.
3. Establish baseline data and sustainability indicators for long-term monitoring.
4. Assess the applicability of the above techniques to other eel fisheries in Australia, in collaboration with NSW. Distribute developed tools via the Australia and New Zealand Eel Reference Group
Biological data and model development for management of longfinned eels
Objectives:
1. Estimate population parameters required for a management model. These include survival, density, age structure, growth, age and size at maturity and at recruitment to the adult eel fishery. Estimate their variability among individuals in a range of habitats.
2. Develop a management population dynamics model and use it to investigate management options.
3. Establish baseline data and sustainability indicators for long-term monitoring.
4. Assess the applicability of the above techniques to other eel fisheries in Australia, in collaboration with NSW. Distribute developed tools via the Australia and New Zealand Eel Reference Group
Stock assessment of the Queensland and New South Wales pearl perch (Glaucosoma scapulare) fishery
Pearl perch (Glaucosoma scapulare) are found commonly in sub-tropical offshore-waters along the east coast of Australia and are a valuable table fish popular with commercial and recreational fishers. The species is long-lived, up to 30 years of age, and reaches sexual maturity at between 25 and 35 cm total length.
Pearl perch are predominantly line-caught and fishing is managed separately by New South Wales (NSW) and Queensland. Historical fishing data indicate that pearl perch harvests have been consistently higher from Queensland waters with 73% of the total catch landed in Queensland in 2013. Approximately 52% of the Queensland catch is taken by recreational fishers compared with 42% in NSW.
In Queensland, the Department of Agriculture and Fisheries (DAF) recently classified the stock status of pearl perch as “transitional depleting” (DAF Stock Status 2015). The status raised concern in both Queensland and NSW as to whether current management arrangements are adequate to protect the sustainability of pearl perch fishery.
This stock assessment incorporates data from both jurisdictions and assesses at the whole of stock level; establishes current stock status reference points including biomass and fishing pressure levels for pearl perch; and provides advice on whether additional management measures are required to reduce fishing pressure and rebuild fish stocks