ライフサイエンスコーパス: fishing

1 amework to a tightly coupled SES, commercial fishing.

2 point for PIPA equivalent to 1.5 y of banned fishing.

3 and four emission scenarios with and without fishing.

4 sing concerns about the ecosystem impacts of fishing.

5 l fishing but increasing during recreational fishing.

6 venues and were also more likely to continue fishing.

7 a long-term decrease in harvest due to over-fishing.

8 t the population level appeared resilient to fishing.

9 y occupation affected their participation in fishing.

10 ime points to examine how illness influenced fishing.

11 nthropogenic stressors such as pollution and fishing.

12 of marine reserves, areas that are closed to fishing.

13 l, structure, and characteristics of illegal fishing.

14 closing large parts of the Pacific Ocean to fishing.

15 monitor, and inform solutions to reduce IUU fishing.

16 ommercial fisheries, communities and vessels fishing a greater diversity of species have less revenue

17 asing specialization over the last 30 years, fishing a set of permits with higher species diversity r

18 s, behavioural changes in GRD in response to fishing activities, and diel overlap between GRD and fis

19 e main prey item and also during the peak of fishing activities, in the rainy season.

20 The nylon fibers appear to be from human fishing activities, suggesting options for management.

21 xes by which fishers in Alaska can diversify fishing activities.

22 ho depend on diverse and largely unregulated fishing activities.

23 1-2016), and develop a system for predicting fishing activity accounting for oceanic variables, clima

24 Concurrently, mass disruptions to fishing activity are common following disasters such as

25 Linking pelagic habitat to fishing activity provides high-resolution decision aids

26 a high-resolution dataset of satellite-based fishing activity to show that anticipation of an impendi

27 among dolphins exposed to anthropopressure (fishing activity), risking social behaviour impairment i

28 activities, and diel overlap between GRD and fishing activity.

29 reduces individual revenue variability, and fishing an additional permit is associated with higher r

30 a historical period dominated by commercial fishing and a contemporary period when commercial fishin

31 c and environmental impacts of provisions of fishing and agricultural capital, with and without enfor

32 ory changes may reduce fishes' resilience to fishing and ecosystems' resistance to environmental vari

33 This suggests that local factors such as fishing and pollution are having minimal effects or that

34 rios due to the cumulative effect of reduced fishing and predation mortalities cascading through the

35 om shoelaces to the knots used for climbing, fishing and sailing(1).

36 Illegal, unreported and unregulated (IUU) fishing and seafood supply chain fraud are multifaceted

37 An integrated ecosystem model including fishing and the impact of rising temperatures, relative

38 d to societies including coastal protection, fishing, and cultural practices.

39 subsistence lifestyle of hunting, gathering, fishing, and farming with few cardiovascular risk factor

40 r efficiency is highly variable, impacted by fishing, and will decline with climate change.

41 MAX model suggested was linked to changes in fishing; and the Norwegian trench region displayed an in

42 ept study using an in silico/in vitro target fishing approach on the fungal secondary metabolite atro

43 f orphan compounds using a so-called "target fishing" approach.

44 ns as proportions of fishing time (days) and fishing area (spatial cells).

45 ectivity patterns of the EIE with industrial fishing areas and coastline regions of the Pacific basin

46 urrents and that their potential benefits to fishing areas are presently limited, since countries wit

47 nal concentration of fishing effort, size of fishing areas, density of vessels, their mobility and th

48 The emergence of longline fishing around the world has been concomitant with an in

49 Using termite fishing as a window into the richness of chimpanzee cult

50 Illness among individuals who listed fishing as their primary occupation affected their parti

51 y can be altered by a switch to recreational fishing, as well as stocking and invasive species.

52 pulations, especially if combined with shark fishing bans.

53 We provide a national illegal fishing baseline for Chile, estimating illegal activity

54 ed; and illegal, unregulated, and unreported fishing becomes more sophisticated.

55 classify these characteristics into discrete fishing behavioral types (FBTs), determining that 3 type

56 etwork contacts are more strongly related to fishing behaviors than ethnicity.

57 e providing poor fishing households with new fishing boats (fishing capital) that can be used further

58 ends not only on the magnitude of changes in fishing but also on the pace at which changes are impose

59 some extent FiB) declining during commercial fishing but increasing during recreational fishing.

60 from density dependence post-harvest, and a fishing-by-warming interaction that decreased diversity

61 pecies and their associated fauna [1], while fishing can alter coastal food webs, reduce biodiversity

62 onary responses to intensive, size-selective fishing can rapidly and continuously destabilize and deg

63 o limit fishing pressure rather than enhance fishing capacity.

64 r fishing households with new fishing boats (fishing capital) that can be used further offshore as a

65 Using a repeated cross-sectional survey of fishing captains to assess potential social impacts of t

66 ng and a contemporary period when commercial fishing ceased and recreational fishing effort increased

67 Median HIV prevalence was higher in fishing communities (42%, range 38-43) than in trading (

68 Although fishing communities (FCs) in Uganda are disproportionate

69 years in four high-prevalence Lake Victoria fishing communities and 36 neighbouring inland communiti

70 ial and ecological data from five coral reef fishing communities in Kenya; including interviews with

71 , and 8.63 in those aged 20-24 years), among fishing communities in Uganda (12.40 per 100 person-year

72 nation HIV interventions in HIV-hyperendemic fishing communities is feasible and could have a substan

73 and low use of combination HIV prevention in fishing communities make these populations a priority fo

74 Here, we add nine termite-fishing communities not studied before, revealing 38 dif

75 of people aged 15-49 years residing in four fishing communities on Lake Victoria.

76 isheries catch and revenue data from Alaskan fishing communities over 34 years to test whether divers

77 ificantly higher in men than in women and in fishing communities than in other community types.

78 significantly lower in both men and women in fishing communities than in trading (age-adjusted preval

79 s depend on the extent to which markets link fishing communities to outside regions through trade.

80 In a cluster-randomized trial in 26 Ugandan fishing communities we investigated effects of community

81 (2703 [13.7%] in inland and 2439 [40.1%] in fishing communities).

82 impact in high-schistosomiasis-transmission fishing communities, in the absence of other interventio

83 e conducted a cluster-randomised trial in 26 fishing communities, Lake Victoria, Uganda.

84 uption were pervasive throughout New England fishing communities.

85 ed in agrarian, 3318 in trading, and 3870 in fishing communities.

86 heries approaches, while supporting thriving fishing communities.

87 For a Philippine fishing community that is a net importer of fish, we sho

88 Fishing constrains phenotypic responses of marine fish t

89 growth rate, fish mobility, fish price, and fishing cost) as well as an important aspect of reserve

90 ting the investigation of chimpanzee termite-fishing culture.

91 del development include dynamic scenarios of fishing, cumulative human impacts, and the effects of ma

92 atly between fisheries from 0 to >50% of the fishing days and area.

93 Fishing did not substantially alter the effects of clima

94 d effects on estuarine communities following fishing disruptions and salinity changes caused by a tro

95 mcoe dating back to the 1860s, to examine if fishing down effects are observed in this highly exploit

96 yet do not appear to commonly show the same fishing down response perhaps because time series are to

97 creasing biomass, contrary to predictions of fishing down the food web [7].

98 This effect, described as fishing down the marine food web, is observed when the t

99 ally children misjudge the risk potential of fishing due to their lack of experience.

100 Whereas fishing effects on predators indirectly altered plankton

101 y to have boosted our ancestors' hunting and fishing efficiency [3], marking a major transition in hu

102 Empirical models of fishing effort and bioeconomic simulations explain why q

103 The cumulative effects of fishing effort and interactions among krill-dependent pr

104 actors, we analyzed the effect of illness on fishing effort and methods.

105 to fish, trophic transfer efficiencies, and fishing effort can quantitatively reconcile this contras

106 ity of information on growth, mortality, and fishing effort for devil rays make quantifying populatio

107 imited spatial refuge from current levels of fishing effort in marine areas beyond national jurisdict

108 n commercial fishing ceased and recreational fishing effort increased.

109 nd find that fishers more than doubled their fishing effort once this area was earmarked for eventual

110 able alternative to fishing, such that total fishing effort remains constant (at best).

111 The additional fishing effort resulted in an impoverished starting poin

112 small-scale fisheries, a synthesis of global fishing effort, and plankton food web energy flux estima

113 s C, rather than changes in trophic state or fishing effort, have restructured the pelagic food web o

114 influenced by the seasonal concentration of fishing effort, size of fishing areas, density of vessel

115 et al were improperly scaled to account for fishing effort, thereby invalidating the analysis.

116 to comparing aggregate rent, stock size, and fishing effort, we focus on the occurrence, size, and lo

117 nstructed the evolution of the fleet and its fishing effort.

118 lso associated with significant increases in fishing effort.

119 found limited evidence that illness reduced fishing effort.

120 ween animal movements and distributions, and fishing effort.

121 eases to the seaweed communities and reduced fishing efforts were the primary factors associated with

122 rom the climatic mean decreases county-level fishing employment by 13%, on average.

123 (95% CI: 10% to 22%) decline in county-level fishing employment in New England, beyond the changes in

124 e administrative data documenting individual fishing events to evaluate the economic impact of the ex

125 between years, highlighting how broadly the fishing exploitation efficiently "tracks" oceanic sharks

126 tentially increasing shark susceptibility to fishing exploitation.

127 ies have less revenue variability than those fishing fewer species.

128 We found that the global fishing fleet doubled between 1950 and 2015-from 1.7 to

129 While forced labor in the world's fishing fleet has been widely documented, its extent rem

130 By 2015, 68% of the global fishing fleet was motorized.

131 the fish stock) and human system (the mobile fishing fleet) confound "treated" and "control" areas.

132 f these two monuments on the Hawaii longline fishing fleet.

133 Previous reconstructions of marine fishing fleets have aggregated data without regard to th

134 ntire Spanish and Portuguese longline-vessel fishing fleets show an 80% overlap of fished areas with

135 d tactics are used across disparate regions, fishing fleets, and taxonomic groups.

136 acked movements of pelagic sharks and global fishing fleets, that 24% of the mean monthly space used

137 Derelict fishing gear (DFG) is abundant across the remote North P

138 t study showed that underwater entrapment in fishing gear followed by rapid decompression may cause g

139 Deaths from bycatch drowning of Scaup in fishing gear have significantly decreased in recent deca

140 Incidental capture, or 'bycatch' in fishing gear is a major global threat to sea turtle popu

141 The incidental capture of wildlife in fishing gear presents a global conservation challenge.

142 ection from anthropogenic threats like fixed fishing gear, shipping, and noise pollution.

143 ciated with ship strikes and entanglement in fishing gear.

144 Because many fishing gears are nonselective, and the costs of making

145 ding the probabilities of dying in different fishing gears.

146 douin's gull, that die in different types of fishing gears: longlines, gillnets and sport trolling, r

147 Commercial fishing generally removes large and old individuals from

148 Fishing glasses should be worn not only for UV protectio

149 y (SBNMS) in the Gulf of Maine is a historic fishing ground renowned for remarkable productivity.

150 in convergence zones that coincide with the fishing grounds of the Hawai'i-based pelagic longline fi

151 urbance event which closed the most-utilized fishing grounds, explorers benefited significantly from

152 within MPAs as they move outside to adjacent fishing grounds.

153 more of locally produced larvae to adjacent fishing grounds.

154 e and qualitative trends within the longline fishing grounds.

155 Our results indicate that recreational fishing had large effects on fish populations that casca

156 estabilize and degrade ecosystems even after fishing has ceased.

157 Our results reveal the profound impact that fishing has had on reef shark populations: we observed n

158 Indiscriminate and intense fishing has occurred in many marine ecosystems around th

159 hlight the complex and profound effects that fishing has on marine ecosystems.

160 erviews with 392 rural fishers, we show that fishing has severely depleted a large-bodied keystone fi

161 ch waters, but climate change and industrial fishing have depleted forage fish stocks in this system

162 lines in real income benefits of 2-63%, with fishing households suffering the largest declines.

163 Many developing countries are providing poor fishing households with new fishing boats (fishing capit

164 In size-structured aquatic ecosystems, fishing impacts are commonly quantified using size spect

165 otential for developing our understanding of fishing impacts in coral reef ecosystems.

166 Yet how krill fishing impacts nutrient fertilisation and the carbon si

167 are a commonly applied tool to reduce human fishing impacts on marine and coastal ecosystems.

168 used to help reduce biologically significant fishing impacts on small cetaceans.

169 form an ecosystem-based approach to managing fishing impacts.

170 which closes 80% of their EEZ to commercial fishing in 2020.

171 Concerns over increased fishing in concentrated areas and ongoing efforts to est

172 ndemic molluscs began well before commercial fishing in Lake Tanganyika, Africa's deepest and oldest

173 At the same time, intensive fishing in regions where rivers are already degraded by

174 in community metrics exceeded the effects of fishing in this highly dynamic study site, suggesting th

175 We suggest that termite fishing in wild chimpanzees shows some elements of cumul

176 rom catch data, mean trophic level (MTL) and fishing-in-balance (FiB), and compared trends between a

177 ion is dominated by litter from the regional fishing industry (83%) and flip-flops from further afiel

178 t an historical account of the growth of the fishing industry and an update on the status of fish pop

179 ds used to routinely assess freshness in the fishing industry reflect more a state of spoilage than a

180 the impacts of these protected areas on the fishing industry, but there has been no ex post empirica

181 had little, if any, negative impacts on the fishing industry, corroborating ecological models that h

182 riment that created a controlled gradient of fishing intensity and assessed the immediate impacts and

183 Commercial fishing is a dangerous occupation despite decades of reg

184 e illegal, unreported, and unregulated (IUU) fishing is a premier issue facing ocean sustainability,

185 and that survivability of returns from creel fishing is high.

186 d intensity of age truncation indicates that fishing is likely reducing the stability of many marine

187 s are too short to witness early depletions, fishing is often recreational, or other factors like sto

188 pressure but also more prone to recovery as fishing is reduced.

189 Fishing is widely considered a leading cause of biodiver

190 ental-contact recreation (boating, canoeing, fishing, kayaking, and rowing) on waterways in the Chica

191 ive evidence linking climate variability and fishing labor has important implications for management

192 d distributions worldwide, yet its impact on fishing labor has not been examined.

193 rticular due to climate change but also from fishing, land-based pollution and shipping.

194 which earns much of its GDP by selling tuna fishing licenses to foreign nations.

195 supercoiled natural rubber fibers and coiled fishing line fibers that cool when stretched.

196 were caught by trawl fishing, longlining and fishing line from December 2012 to October 2013.

197 al rubber, nickel titanium, and polyethylene fishing line.

198 We analysed tensile properties of the fishing lines of the New Zealand glowworm Arachnocampa l

199 C, relative humidity of 98%) whereby the wet fishing lines only show a bonding ability at high relati

200 Pufferfish were caught by trawl fishing, longlining and fishing line from December 2012

201 Without fishing, mean global animal biomass decreased by 5% (+/-

202 Instead, ill fishers shifted their fishing methods.

203 The model is driven solely by fishing mortality and climatic variables and based on ti

204 Our analysis of adult fishing mortality and spawning stock biomass of 22 North

205 that both the temporal and spatial scales in fishing mortality and spawning stock biomass were equiva

206 ularly influential in whether stock size and fishing mortality are currently in or trending toward de

207 individual movement traits can contribute to fishing mortality of sharks found within MPAs as they mo

208 imized management, or an arbitrarily defined fishing mortality outside the MPA's boundaries.

209 y partially substantial reductions (>50%) in fishing mortality resulting from small increases in MPA

210 ge at maturity, maximum age, and natural and fishing mortality.

211 he management systems by species of 28 major fishing nations and examined influences of economic, geo

212 Proximity to active fishing net also had a pronounced effect on state occupa

213 seals foraging was highest <5 km from active fishing nets (51%) and decreased as distance to nets inc

214 However, seals used sites <5 km from active fishing nets only 3% of their time at sea highlighting a

215 ronmental covariates and proximity to active fishing nets within a multivariate hidden Markov model (

216 In the Caribbean, over-fishing of large herbivorous fish and disease among the

217 sing use of the deep ocean (e.g., for bottom fishing, oil and gas extraction, and deep-seabed mining)

218 anagement measures that reduce the impact of fishing on age truncation, including no-take areas, slot

219 ing no-take areas, slot limits that prohibit fishing on all except a narrow range of fish sizes, and

220 s in environmental conditions and commercial fishing on annual adult survival and use two-sex matrix

221 policies less likely to mitigate impacts of fishing on habitats and ecosystems compared with the lab

222 h less healthy stocks and greater impacts of fishing on other species.

223 els evaluating the effects of size-selective fishing on these patterns had only small support.

224 ification and turnover in the composition of fishing opportunities increased economic stability durin

225 ls are required to travel further afield for fishing opportunities.

226 tions of "scorched earth" (i.e., severe over-fishing), optimized management, or an arbitrarily define

227 of cephalopod catch rates (catch per unit of fishing or sampling effort).

228 in-vitro selection technique (BLI-SELEX) for fishing out specific aptamers against E. coli Shiga toxi

229 But they show that climate can impact fishing outcomes in ways unaccounted by management and o

230 ent an EEZ-wide analysis of Palau commercial fishing over a 6-year period (2011-2016), and develop a

231 Other, more prolific species can withstand fishing over the long term if catches are subject to eff

232 The role of fishing patterns in explaining between-fisheries variati

233 system integrity and resilience from current fishing patterns than previously recognized.

234 idged by borrowing quota from the subsequent fishing period or transforming unutilized quota in other

235 We project that fishing practices could be modified to increase total ca

236 degraded by coastal development, destructive fishing practices, and climate change.

237 roducts, drives unregulated and exploitative fishing practices, which are in turn facilitated by the

238 an disturbance and provide guidance for best fishing practices.

239 ecosystem more prone to coral collapse under fishing pressure but also more prone to recovery as fish

240 the response of the ecosystem to changes in fishing pressure depends not only on the magnitude of ch

241 Water quality and fishing pressure had minimal effect on the unprecedented

242 Fishing pressure is disproportionately concentrated insi

243 but not causally correlated, revealing that fishing pressure is most intense in rivers where potenti

244 ensiveness of stock assessments, strength of fishing pressure limits, and comprehensiveness of enforc

245 ecruitment, but local changes in habitat and fishing pressure may have played a role in driving local

246 Fishing pressure on coral reef ecosystems has been frequ

247 re as a means to improve incomes and relieve fishing pressure on nearshore fish stocks.

248 ure climate change and sustainable levels of fishing pressure on selected target species.

249 Mapping and quantifying bottom trawling fishing pressure on the seafloor is pivotal to understan

250 hat have experienced substantial increase in fishing pressure over the past 60 y.

251 rature, oxygen, net primary production and a fishing pressure proxy, to which we apply the EOF and NA

252 hieve management objectives if used to limit fishing pressure rather than enhance fishing capacity.

253 Devil rays (Mobula spp.) face intensifying fishing pressure to meet the ongoing international deman

254 n and parrotfish, which escaped die-offs and fishing pressure, can achieve abundances comparable to t

255 this effect depended on local abundances and fishing pressure, with MPAs required to be 1.6-2.6 times

256 ch actions, recognizing the widely differing fishing pressures and conservation capacity.

257 ol skills by providing learners with termite fishing probes.

258 Fishing rates of a small-scale artisanal Mexican fishery

259 Analysis of our fishing records and available literature, however, sugge

260 ne Protected Area along the Peninsula, a key fishing region, is driving the development of an adaptiv

261 ral capital, with and without enforcement of fishing regulations that prohibit the use of larger vess

262 nt to an average of USD 77 billion in annual fishing revenue.

263 rsification levels, trends, and variation in fishing revenues changed after implementation of catch s

264 ted whether diversification and variation in fishing revenues changed after implementation of catch s

265 More than 85% of communities show reduced fishing revenues following these regime shifts.

266 s a competitive race to fish that compresses fishing seasons, resulting in ecological damage, economi

267 ind strong evidence that catch shares extend fishing seasons.

268 direction and intervention for the artisanal fishing sector in these challenging times.

269 egional catch and revenue in the New England fishing sector, but also ultimately county-level wages a

270 text indicates that one of these sites was a fishing settlement for the procurement of local catches,

271 fter a US-Russia war under business-as-usual fishing-similar in magnitude to the end-of-century decli

272 agrarian (n=27), trading (n=9), or lakeside fishing sites (n=4).

273 t the paternal-effort hypothesis in the dark fishing spider, Dolomedes tenebrosus.

274 s that fishers have no viable alternative to fishing, such that total fishing effort remains constant

275 After "fishing" them from the blood, the cells, still bound to

276 uncements were to trigger similar preemptive fishing, this could temporarily increase the share of ov

277 Orcinus orca) interactions as proportions of fishing time (days) and fishing area (spatial cells).

278 For example, quickly increasing fishing to a given level can collapse an ecosystem that

279 ulations, from direct top-down management of fishing to indirect improvement of governance conditions

280 approach to compare the qualities of termite fishing tools used by wild chimpanzees by comparing the

281 tes of the intensity of ship activity across fishing, tourism and research sectors: there may be appr

282 shery, a fisherman's probability of taking a fishing trip in high wind conditions decreased by 82% co

283 vessel position records from 2494 commercial fishing trips along with corresponding revenues, here we

284 can be deployed to perform on-farm assays in fishing units.

285 , we describe an outbreak of SARS-CoV-2 on a fishing vessel associated with a high attack rate.

286 ustrial fisheries have expanded globally, as fishing vessels are required to travel further afield fo

287 Fishing vessels attracted more birds than other vessels,

288 estimation of the proportion of nondeclared fishing vessels operating in national and international

289 existed for remotely identifying individual fishing vessels potentially engaged in these abuses on a

290 lity due to lethal interactions with illegal fishing vessels.

291 -eight marine turtles were examined on-board fishing vessels.

292 ustrial longliner, squid jigger, and trawler fishing vessels.

293 domized 26 high-schistosomiasis-transmission fishing villages in Lake Victoria, Uganda, in a 1:1 rati

294 em, but there were negative perceptions when fishing was being prohibited.

295 Previously, termite fishing was known from eight locations with two distingu

296 g a pull-down assay based on mixed disulfide fishing, we characterized the thiol-dependent interactom

297 Analogous to trawl fishing, we introduced multiple Hg binding units (thymin

298 Our results support suspending fishing when prey biomass drops below critical threshold

299 electric eels (Electrophorus electricus) by "fishing with horses" [von Humboldt A (1807) Ann Phys 25:

300 tween 20 degrees S and 40 degrees S, and the fishing zone within international waters off Peru (20 de