ライフサイエンスコーパス: fishing

1 merged into one automated procedure called "FISHing".

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

3 nthropogenic stressors such as pollution and fishing.

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

5 ressure to protected areas with little to no fishing.

6 istic of the life-history changes induced by fishing.

7 ess and used by many people for swimming and fishing.

8 eristics and therefore, likely attributed to fishing.

9 opment, agricultural runoff, oil spills, and fishing.

10 tic environments, especially under intensive fishing.

11 with area-focused human activities, such as fishing.

12 the effects of completely closing the HS to fishing.

13 rds from historical baselines as a result of fishing.

14 conservation outcomes than does a HS open to fishing.

15 tially reduce the variability of income from fishing.

16 ncludes top-down ecosystem depletion through fishing.

17 complex tool use task that simulated termite fishing.

18 reatened by other human disturbances such as fishing.

19 re compared to evaluate ecosystem effects of fishing.

20 a Bay and the Delta region) remain closed to fishing.

21 t the population level appeared resilient to fishing.

22 y occupation affected their participation in fishing.

23 ime points to examine how illness influenced fishing.

24 ious sectors including sex work (329 [32%]), fishing (275 [27%]), and factories (136 [13%]).

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

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

27 ho depend on diverse and largely unregulated fishing activities.

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

29 ded turtles vs. those caught as bycatch from fishing activity, suggesting that stranded animals are n

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

31 Fishing and climate change impact the demography of mari

32 Target-fishing and drug responsive target stability experiments

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

34 ery times, despite predictable influences of fishing and life history.

35 t many parasites play in marine communities, fishing and other human impacts could exert cryptic but

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

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

38 Supply chains of one krill fishing and processing company, Aker BioMarine of Norway

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

40 BA (Brazil), a region which carciniculture, fishing and shellfish extraction are the most important

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

42 ions of C. othonopterus during 21-25 days of fishing and within an area of 1,149 km(2) of a biosphere

43 reased due to changes in abundance caused by fishing and, alternatively, where productivity shifted b

44 likely benefiting from greater resilience to fishing and/or climate change.

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

46 is Illegal, Unreported and Unregulated (IUU) fishing, and there is now an increased emphasis on the u

47 licts among offshore wind energy, commercial fishing, and whale-watching sectors in Massachusetts and

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

49 A network fishing approach with the kinase hits identified other k

50 Many of the species most threatened by fishing are caught in multispecies fisheries, which can

51 Threats to species from commercial fishing are rarely identified until species have suffere

52 Spawning and fishing are synchronized on a semi-lunar cycle, with pea

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

54 om commercially and recreationally important fishing areas in the Baltic Sea, freshwater lakes, and f

55 lions of small-scale fishers--and identifies fishing areas where, given the evidence of cumulative ho

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

57 We show that landing the entire catch while fishing as usual has conservation penalties for seabirds

58 ass were related to the intensity of lobster fishing (as indicated by the density of traps pulled).

59 resident reef fish biomass in the absence of fishing (B0) averages approximately 1,000 kg ha(-1), and

60 pulations, especially if combined with shark fishing bans.

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

62 proportion of ARS behaviours associated with fishing boats were higher for males (81%) than females (

63 s (i.e. illegal, unreported, and unregulated fishing) but will also provide a basis to transform curr

64 These data indicate that fishing can drive declines in parasite abundance at the

65 basis and associated impacts by showing how fishing can increase fluctuations in fishes and their ec

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

67 on is high, seemingly conservative levels of fishing can still precipitate a severe decline in the he

68 Fishing can trigger trophic cascades that alter communit

69 Fishing can, thereby, have far reaching consequences on

70 o limit fishing pressure rather than enhance fishing capacity.

71 e impacts to marine ecosystems globally from fishing, climate change, and ocean- and land-based stres

72 environment became increasingly impacted by fishing, climate change, habitat degradation and other a

73 ce of commercial fish species since deep-sea fishing commenced in the 1970s.

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

75 was collected during an interview survey of fishing communities across the middle-lower Yangtze drai

76 system service benefits across 28 coral reef fishing communities in four countries.

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

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

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

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

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

82 ely impacted by spatial restrictions, is the fishing community.

83 >25% and more than doubled the revenue from fishing, compared with earlier versions based on stakeho

84 with nonspatial management, particularly if fishing costs are low, although profit increases availab

85 rn California kelp forests, and that lobster fishing does not always catalyze a top-down trophic casc

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

87 ng body mass or trophic level, representing 'fishing down the food web', accentuates prey-release eff

88 in central Chile to assess the influence of fishing-driven biodiversity loss on parasites of exploit

89 n contrast with recent analyses that suggest fishing drives increased fluctuations by changing intrin

90 Whereas fishing effects on predators indirectly altered plankton

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

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

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

94 ility, as well as the potential for reducing fishing effort and sustaining fisheries.

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

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

97 ted areas, indicating that redistribution of fishing effort has not severely affected unprotected pop

98 Because fishing effort imposes a common source of mortality on a

99 user rights, will affect the distribution of fishing effort in a more nuanced manner.

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

101 iple self-interested actors distribute their fishing effort to maximize their individual economic gai

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

103 Over this time period, domestic fishing effort, as numbers of hooks set in the core Hawa

104 es across the Caribbean region, we show that fishing effort, human density and thermal stress anomaly

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

106 ng pressure were associated with declines in fishing effort.

107 this pattern well as a response to increased fishing effort.

108 ity outside marine reserves due to displaced fishing effort.

109 found limited evidence that illness reduced fishing effort.

110 Without further processing the resulting FISHing eluates are suitable for BEAMing (beads, emulsio

111 al allocation of fishing quota to vessels or fishing entities, also called catch shares) can improve

112 d and demonstrate elements of a statistical 'fishing exercise', that is the carrying out of a huge nu

113 , post hoc analyses (i.e., "data dredging," "fishing expeditions," or "P-hacking").

114 odel incorporating egg predation and herring fishing explains the major population trends of Georges

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

116 tentially increasing shark susceptibility to fishing exploitation.

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

118 s increase depends on characteristics of the fishing fleet and target species.

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

120 d find evidence of cumulative impacts across fishing fleets and gears.

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

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

123 gement actions was unequally divided between fishing fleets; the loss of value from finfish gillnet f

124 avily fished sites, supporting the idea that fishing for lobsters releases top-down control on urchin

125 receptor HasR, and the heme-free apoprotein fishing for new porphyrin to be taken up after the heme

126 cked appear to be most vulnerable to pelagic fishing gear deployed from 0-125 m depths, which they ma

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

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

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

130 e gillnets, shrimp driftnets and introduce a fishing gear that has no vaquita bycatch.

131 ng in poor weather, overloading vessels with fishing gear, and neglecting maintenance.

132 tal care, also affect their vulnerability to fishing gear.

133 ciated with ship strikes and entanglement in fishing gear.

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

135 a from the three most commonly used types of fishing gears worldwide.

136 ding the probabilities of dying in different fishing gears.

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

138 Commercial fishing generally removes large and old individuals from

139 Seafood samples from the fishing ground closure areas of Mississippi Gulf Coast t

140 umbers of hooks set in the core Hawaii-based fishing ground, has increased fourfold.

141 rves do replenish populations in surrounding fishing grounds, while modern reserve networking theory

142 more of locally produced larvae to adjacent fishing grounds.

143 estabilize and degrade ecosystems even after fishing has ceased.

144 losing the high-seas enclaves to purse seine fishing has negligible effect on the BET biomass.

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

146 Closing the former to fishing has recently been proposed in the literature and

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

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

149 it from fisheries, greater specialisation of fishing households, or higher rewards from fishing in mo

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

151 ocean management needs to consider not only fishing impacts but drivers of harvest.

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

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

154 ith the earliest archaeological evidence for fishing in Africa.

155 ce populations or reduce it by concentrating fishing in harvested areas.

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

157 f fishing households, or higher rewards from fishing in more economically developed sites due to tech

158 fisheries results in risky behavior such as fishing in poor weather, overloading vessels with fishin

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

160 e seine fishery and restrictions on longline fishing in spawning areas, are the most efficient conser

161 ted areas (MPAs) are established to restrict fishing in specific locations.

162 from this region was the onset of commercial fishing in the late 1800s.

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

164 This shift may be attributed to (i) fishing, including mechanised beam trawling introduced i

165 Phosphopeptide fishing indicated that SOCS6 binds directly to phosphoty

166 mpact of different management options on the fishing industry and can be incorporated into planning s

167 and the possible contribution of the lakes' fishing industry to the spread of cholera.

168 ces also have a broad economic impact on the fishing industry.

169 position on reefs having different levels of fishing intensity across the Caribbean.

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

171 to 2 days before the new and full moon, and fishing intensity and catch are highest at the spawning

172 s of target fish biomass (as an indicator of fishing intensity) and eight metrics of ecosystem state.

173 ever, was positively correlated with lobster fishing intensity, which contradicts the trophic cascade

174 Commercial fishing is a dangerous occupation despite decades of reg

175 tial management in which the distribution of fishing is chosen to maximize profits.

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

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

178 ted to cues from coral-dominated areas where fishing is prohibited.

179 After fishing is reduced or the perturbation ended, this low p

180 Fishing is the primary source of diminished reef functio

181 Fishing is widely considered a leading cause of biodiver

182 Fishing is widely known to magnify fluctuations in targe

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

184 imming are often used for boating, canoeing, fishing, kayaking, and rowing.

185 ironment, (i) the addition of mortality from fishing leads to increased temporal variability for all

186 ensive high-strength polymer fibers used for fishing line and sewing thread can be easily transformed

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

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

189 f a well-studied lake ecosystem, we show how fishing may both increase fluctuations in fish abundance

190 Instead, ill fishers shifted their fishing methods.

191 Furthermore, we demonstrate how fishing modifies the dynamics and show that the sardine

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

193 ho and those differences depend on lifespan, fishing mortality and recruitment variations.

194 arvested populations, in which variations in fishing mortality and recruitment will affect age-struct

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

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

197 driven to local extinction at low levels of fishing mortality and that a similar degree of protectio

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

199 The combined fishing mortality by all gears will soon reduce the BET

200 Simulations show that a drastic reduction in fishing mortality has resulted in a doubling of the tota

201 The optimal fishing mortality is almost identical for the evolutiona

202 However, if fishing mortality is as high as it has been historically

203 recovery of spawner escapement requires that fishing mortality is significantly reduced; and (iv) the

204 Fish stocks experiencing high fishing mortality show a tendency to mature earlier and

205 show that the recent sustained reduction in fishing mortality, facilitated by the implementation of

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

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

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

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

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

211 Here, we test how fishing on Caribbean coral reefs influences biodiversity

212 tch shares caused the average annual rate of fishing on high wind days to decrease by 79%.

213 by the spill have been impacted by deep-sea fishing operations.

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

215 With this hypothesis, an increase in fishing or a natural perturbation can drive a population

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

217 by the periodicity of human activities like fishing or traveling.

218 individual to fish sustainably, curb illegal fishing, or create large marine reserves as steps to enh

219 ilayer in the same orientation for efficient fishing out of the membrane by smAFM.

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

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

222 ultiple indicators are necessary to identify fishing perturbations.

223 ns in important species of fish from various fishing ports of the southern Kingdom of Morocco (Sardin

224 Historical records of this fishing practice date back to the mid-1300s.

225 ny initiatives aimed at tackling destructive fishing practices and promoting the sustainability of fi

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

227 ombining landing obligations with changes in fishing practices to limit the capture of unwanted fish

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

229 an disturbance and provide guidance for best fishing practices.

230 und the turn of the century: since then, the fishing pressure (as measured by the exploitation rate)

231 ocations with strongly contrasting levels of fishing pressure (Cayman Islands and Jamaica; Curacao, B

232 mental importance of both climate change and fishing pressure for our understanding of changing distr

233 t of common and unique characteristics: high fishing pressure for several years before collapse, a sh

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

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

236 teracting effects of climate change and high fishing pressure lead to dramatic spatiotemporal changes

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

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

239 likely additional impact that high levels of fishing pressure might have on distribution.

240 Fishing pressure on coral reef ecosystems has been frequ

241 ive that incorporates predictable impacts of fishing pressure on ecosystem function is imperative for

242 d on the success of a major reduction in the fishing pressure on European fish stocks.

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

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

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

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

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

248 Evaluation of the candidate indicators for fishing pressure showed that indicators at the community

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

250 ese communities span a gradient from extreme fishing pressure to protected areas with little to no fi

251 The reductions in fishing pressure were associated with declines in fishin

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

253 ncrease outside of MPAs is due to changes in fishing pressure, fisheries management actions, adult sp

254 ver, the eastward shift is best explained by fishing pressure, suggestive of significant depletion of

255 roductivity, and a lagged response to reduce fishing pressure.

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

257 ifaceted effects of environmental change and fishing pressures in different regions of the North Sea.

258 zees manufacture sophisticated, brush-tipped fishing probes from specific raw materials, teaching in

259 ol skills by providing learners with termite fishing probes.

260 ies management (the individual allocation of fishing quota to vessels or fishing entities, also calle

261 Fishing rates of a small-scale artisanal Mexican fishery

262 Given protection from fishing, reef fish biomass has the potential to recover

263 l habitat and increase revenues from lobster fishing relative to current management.

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

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

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

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

268 ind strong evidence that catch shares extend fishing seasons.

269 ifferent degrees of development, ecosystems, fishing sectors and type of resources.

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

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

272 We compare competitiveness in traditional fishing societies where local natural forces determine w

273 an black bears assessed whether each mode of fishing (solo vs. paired) occurs mainly where it is most

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

275 or fishermen wishing to maintain diversified fishing strategies.

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

277 Fishing takes place in the high seas and Exclusive Econo

278 Estuaries provide critical hunting and fishing territory for these populations, and, until rece

279 g-term sustainability gains in shrimping and fishing that result from mangrove protection.

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

281 re fecund fish are preferentially removed by fishing, there is no empirical evidence describing the r

282 To evaluate whether fishing triggered a trophic cascade we pooled data acros

283 l on urchins and macroalgae, and (2) lobster fishing triggers a trophic cascade leading to increased

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

285 y the combustion of fossil fuels onboard the fishing vessel and a transport/resupply vessel.

286 gannet Morus bassanus[3], to investigate how fishing vessels affect individual birds' behaviours in n

287 We document the footprint of fishing vessels' (>/=15 m length) influence on foraging

288 ng, but only 42% of ARS were associated with fishing vessels, indicating much 'natural' foraging.

289 assanus revealed that all birds photographed fishing vessels.

290 hypothesis that in heavily helminth-exposed fishing villages on Lake Victoria, Uganda, helminth infe

291 e, 5-29 years) residing in high-transmission fishing villages or a moderate-transmission village, wor

292 However, disentangling the contributions of fishing vs. natural processes on population dynamics has

293 Once an area closed to fishing was free of visibly floating oil and all sensory

294 Yet, the ratio of paired versus solo fishing was significantly lower than either profitabilit

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

296 A risk-based management scheme that reduces fishing when populations become scarce would protect for

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

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

299 foreign body was identified as an artificial fishing worm by morphological comparison to a similar co

300 We find that completely closing the HS to fishing would simultaneously give rise to large gains in