ライフサイエンスコーパス: aquatic

1 od, and there are no indications that it was aquatic, amphibious, or unusual with respect to the ecol

2 f the genus, a group known to infect several aquatic and hematophagous taxa.

3 y promotes V. cholerae's survival during its aquatic and host life cycles, but also influences its ev

4 d waste treatment (CWT) plants pose risks to aquatic and human health.

5 ptors that bioaccumulate in and are toxic to aquatic and other organisms.

6 echanisms by which natural organic matter in aquatic and soil environments may play an important role

7 led insights into oxygen dynamics in various aquatic and terrestrial environments and in the inherent

8 ources, seriously affecting the terrestrial, aquatic, and aerial flora and fauna.

9 spatial patterns occur in many terrestrial, aquatic, and marine ecosystems.

10 theory-based method, on both terrestrial and aquatic animal data (U.S. Breeding Bird Survey and marin

11 ntrast, the aquaculture industry was farming aquatic animals at CO2 levels that far exceed end-of-cen

12 Despite this, many aquatic animals consistently orient and swim against onc

13 Such tissues can be directly examined in aquatic animals, providing valuable opportunities for th

14 ly important cause of diseases in humans and aquatic animals.

15 about the developmental impact on nontarget aquatic animals.

16 piratory function and aerobic performance in aquatic animals.

17 The preservation of aquatic arthropods in amber is unusual but offers a uniq

18 Soil, aquatic, atmospheric, animal-associated, and built ecosy

19 al components of functional gene dynamics in aquatic bacterial metacommunities.

20 The aquatic bacterium and human intestinal pathogen, Vibrio

21 Vibrio vulnificus is a Gram-negative aquatic bacterium first isolated by the United States (U

22 ttranslational regulation of sigma(S) in the aquatic bacterium Shewanella oneidensis involves the Crs

23 rse biotic media and passive sampler phases; aquatic baseline toxicity; and relevant diffusion coeffi

24 species abundance and richness of colonizing aquatic beetles are determined by patch quality and cont

25 n drive multi-scale colonization dynamics of aquatic beetles through the processes of contagion and c

26 s, and assayed colonization by 35 species of aquatic beetles.

27 Finally, the local aquatic benefits of grass swales and bioswales offset gl

28 l changes in conservation efforts addressing aquatic biodiversity and fishery resources in the centra

29 sk assessment of pesticides fails to protect aquatic biodiversity.

30 hat have been widely detected in house dust, aquatic biota, surface water, and wastewater environment

31 rived microplastics, particularly fibers, on aquatic biota.

32 ds for discharge of wastewater effluent into aquatic bodies are becoming more stringent, requiring so

33 close connection between the terrestrial and aquatic C cycle.

34 relatively large resilience of the source of aquatic C export to forecasted hydroclimatic changes.

35 The age of aquatic C in runoff varied little throughout the year an

36 only 5% of the landscape, we estimate that aquatic C. aquatilis and A. fulva account for two-thirds

37 Aquatic chytrid fungi threaten amphibian biodiversity wo

38 uaries) or acidic (e.g., acid rain droplets) aquatic conditions or both.

39 litter subsidies are important resources for aquatic consumers like tadpoles and snails, causing bott

40 n ((1)O2), contributes to the degradation of aquatic contaminants and is related to an array of DOM s

41 potential of IL cations to become persistent aquatic contaminants.

42 an enhanced tactile function utilised in an aquatic context, so far in pliosaurids, the Cretaceous t

43 the most significant flux of the land-ocean aquatic continuum, and of a similar magnitude as emissio

44 of this sample suggests a mixed terrestrial/aquatic diet.

45 r) for resolving complex mixtures of natural aquatic dissolved organic matter (DOM) and compared this

46 Aquatic ecological responses to climatic warming are com

47 onmental problem affecting public health and aquatic ecological sustainability.

48 e regarded as potential miniature models for aquatic ecology, but detailed investigations of their mi

49 moting the integration of chytrid fungi into aquatic ecology.

50 ersheds threaten drinking water supplies and aquatic ecology.

51 nisms is emerging as a fundamental aspect of aquatic ecology.

52 nagement because of corresponding effects on aquatic ecosystem functioning, drinking water resources

53 sk assessment of pesticides fails to protect aquatic ecosystem health.

54 ty generation extends the potential risk for aquatic ecosystem impacts beyond U.S. borders.

55 obial assembly might be beneficial to adjust aquatic ecosystem structure and function.

56 the high risk posed by this compound to the aquatic ecosystem.

57 cene is critical to protecting and restoring aquatic ecosystems and ensuring human water security.

58 e negative impacts of elevated CO2 on future aquatic ecosystems and the sustainability of fish and sh

59 w of the way in which vitamins are cycled in aquatic ecosystems and their importance in structuring p

60 ng water quality, biogeochemical cycles, and aquatic ecosystems are estimated to cost US$210 billion

61 Aquatic ecosystems are expected to receive Ag(0) and Ag2

62 s that can reduce future impacts to regional aquatic ecosystems as they grow.

63 Aquatic ecosystems depend on terrestrial organic matter

64 nic stressors and those of natural origin on aquatic ecosystems have intensified the need for predict

65 ed, but their frequency, size, and impact on aquatic ecosystems have not been quantified.

66 ining links among forests, organic soils and aquatic ecosystems in a changing climate will become inc

67 acts such as climate change and pollution on aquatic ecosystems is critical.

68 Closing nutrient loops in terrestrial and aquatic ecosystems is integral to achieve resource secur

69 cessful clade of marine reptiles abundant in aquatic ecosystems of the Mesozoic, inhabited nearshore

70 the temperature dependence of respiration in aquatic ecosystems remain uncertain.

71 These findings suggest that exposure of aquatic ecosystems to individual pesticides or their mix

72 Diatoms are widespread in aquatic ecosystems where they may be limited by the supp

73 n the functional linkage of organic soils to aquatic ecosystems whereby they can help buffer the effe

74 nce suggests the ubiquity of microplastic in aquatic ecosystems worldwide, our knowledge of its distr

75 diversity of chytrids across a wide range of aquatic ecosystems worldwide.

76 nities of zooplankton, a critical portion of aquatic ecosystems, can be adversely affected by contami

77 In size-structured aquatic ecosystems, fishing impacts are commonly quantif

78 etection of genetic material from species in aquatic ecosystems, including environmental DNA (eDNA),

79 In aquatic ecosystems, the cycling and toxicity of nickel (

80 In aquatic ecosystems, UV-induced oxidation of terrigenous

81 better insight in how pesticides may affect aquatic ecosystems, we tested how sublethal pesticide co

82 fficient biomonitoring tool to protect local aquatic ecosystems.

83 length and shape over time in these dynamic aquatic ecosystems.

84 nce chemical and biological processes in all aquatic ecosystems.

85 ae play a major role as primary producers in aquatic ecosystems.

86 terest for understanding algal production in aquatic ecosystems.

87 food production, with detrimental impacts on aquatic ecosystems.

88 viral richness are higher for soils than for aquatic ecosystems.

89 ton is crucial for successful restoration of aquatic ecosystems.

90 of primary producers and nutrient cyclers in aquatic ecosystems.

91 s, particularly in birds, in terrestrial and aquatic ecosystems.

92 , livestock forage in grasslands and fish in aquatic ecosystems.

93 tion could thus control the vulnerability of aquatic ectotherms to global warming.

94 dotherms; however, comparable adaptations in aquatic ectotherms, such as fishes, have not been as ext

95 during peak growing season for the dominant aquatic emergent plants in the Alaskan arctic coastal pl

96 the overall toxicity burden than VOCs or any aquatic emission.

97 Aquatic emissions can become larger contributors to the

98 ic necrosis virus (IHNV) as a model to study aquatic enveloped virus diseases and their inhibition.

99 Vibrio species naturally reside in the aquatic environment and a major metabolite in this habit

100 encounters phosphate limitation in both the aquatic environment and human intestinal tract.

101 the cell to control biofilm formation in the aquatic environment and within the human intestine.

102 ulate matter (SPM) is present in the natural aquatic environment as loosely bound aggregates or "floc

103 Microplastic contamination of the aquatic environment is a global issue.

104 d and seamount evolutionary processes in the aquatic environment remain unclear.

105 nvironmental drivers, suggest changes in the aquatic environment that are expected in this ecosystem

106 Cetaceans, a group of mammals adapted to the aquatic environment that descended from terrestrial arti

107 produced by various (micro)algae sharing the aquatic environment with V. campbellii, have a similar e

108 oval pathway of functionalized SWCNTs in the aquatic environment, and that the residual amorphous car

109 y of vanadium controls its occurrence in the aquatic environment, but the impact of vanadium(V) speci

110 In the aquatic environment, the behavior of hydrophobic organic

111 Vibrio cholerae is a natural resident of the aquatic environment, where a common nutrient is the chit

112 intestine and exoskeleton to persist in the aquatic environment.

113 ics and epoxy resins and is prevalent in the aquatic environment.

114 n of the risks of ionizable chemicals in the aquatic environment.

115 lems has led to its common occurrence in the aquatic environment.

116 iology exhibit dramatic adaptations to their aquatic environment.

117 roles of FGFs in cetacean adaptation to the aquatic environment.

118 ylmethane, triclocarban and triclosan in the aquatic environment.

119 sessment strategies for this chemical in the aquatic environment.

120 A new generation of speciation-based aquatic environmental quality standards (EQS) for metals

121 ive of a temporal and spatial exploration of aquatic environments (surface and groundwater), we devel

122 tected by direct contact with the emitter in aquatic environments and are perceived at high doses tha

123 Vibrio cholerae is a natural inhabitant of aquatic environments and converts to a pathogen upon inf

124 antiandrogenicity is frequently observed in aquatic environments and may pose a risk to aquatic orga

125 ified as contaminants of emerging concern in aquatic environments and research into their behavior an

126 and fate of PFOS at oil-water interfaces in aquatic environments as well as the enhanced removal of

127 onicotinoids are inevitably transferred into aquatic environments either via spray drift or surface r

128 Climate change is altering aquatic environments in a complex way, and simultaneous

129 nt and mobile organic contaminants (PMOC) in aquatic environments is a matter of high concern due to

130 he occurrence and ecotoxicity of steroids in aquatic environments is poorly known.

131 sed in personal care products and emitted to aquatic environments through wastewater effluents, and t

132 atile methyl siloxanes (cVMS) are emitted to aquatic environments with wastewater effluents.

133 Two emerging contaminants commonly found in aquatic environments, enrofloxacin (ENRO) and ciprofloxa

134 In future aquatic environments, populations will encounter differi

135 arbon nanotubes (SWCNTs) make their way into aquatic environments, they may reduce the toxicity of ot

136 d as effective phases for the remediation of aquatic environments, to remove anionic contaminants mai

137 ic activity is widespread in terrestrial and aquatic environments, very little is known about the ure

138 eal disease cholera, but it also persists in aquatic environments, where it displays an expression pr

139 th chemicals that are already present in our aquatic environments, which is essential for determining

140 reduction rates ever measured in terrestrial aquatic environments, which we infer to account for a la

141 allowing animals to obtain oxygen in hypoxic aquatic environments.

142 for anticipating climate-related impacts in aquatic environments.

143 d fate of engineered nanoparticles (ENPs) in aquatic environments.

144 used as indicators of terrestrial input into aquatic environments.

145 , which can help determine the fate of Cr in aquatic environments.

146 ciently colonize and dominate in fluctuating aquatic environments.

147 zed role in the ecology of AIVs peridomestic aquatic environments.

148 poxy resins, BPA has entered terrestrial and aquatic environments.

149 s, IL cations have a high potential to reach aquatic environments.

150 sulfur species ever recorded in terrestrial aquatic environments.

151 estrial systems may not be as represented in aquatic environments.

152 ssments of accidental chemical releases into aquatic environments.

153 dressing the current gross under-sampling of aquatic environments.

154 f the World, while excess of soil P triggers aquatic eutrophication in other regions.

155 The aquatic export of C from boreal peatlands is recognized

156 The Chemical Aquatic Fate and Effects (CAFE) database is a tool that

157 taminated sediment risks causing toxicity to aquatic fauna.

158 ehistoric coastal populations for processing aquatic faunal resources is often difficult in archaeolo

159 other useful tool for determining sources of aquatic fecal bacteria.

160 pid metabolism of accumulated OPEs occurs in aquatic feeding birds and may warrant further investigat

161 and biomagnification of microplastics up the aquatic food chain.

162 grazers, significant to the microbial loop, aquatic food webs, and biogeochemical cycling.

163 tion size and trait evolution at the base of aquatic food webs.

164 't be used to exclusively support a model of aquatic foraging in theropods and argue instead that an

165 xceptional sites for studying the ecology of aquatic fungi under conditions of minimal human disturba

166 hat is central to zoospore phototaxis in the aquatic fungus Blastocladiella emersonii It has generate

167 RhoGC is a fusion protein from the aquatic fungus Blastocladiella emersonii, combining a ty

168 Our sampling of fish biodiversity and aquatic habitat along ten 3-km sites within the Upper Ne

169 These aquatic habitats are often embedded within and around ag

170 Aquatic habitats comprise of interconnected waterways, a

171 Thus far, studies in aquatic habitats on the utilization of methylamine, the

172 Container aquatic habitats support a specialized community of macr

173 thrin) on microbial communities of container aquatic habitats.

174 NIS and therefore favour invasive species in aquatic habitats.

175 centrations) in developed watersheds present aquatic health concerns, given their acknowledged potent

176 r source characterized by a high fraction of aquatic humic matter.

177 The aquatic impacts of anthropogenic land use are often firs

178 on how numerically and functionally dominant aquatic insect species respond to changes in stream temp

179 Two aquatic insects - the meltwater stonefly (Lednia tumana)

180 biomonitoring, including early detection of aquatic invasive species (AIS).

181 ing pressure by quagga mussels, a widespread aquatic invasive species.

182 ial and their CYP inhibition strength in the aquatic invertebrate Gammarus pulex.

183 Aquatic invertebrates (chironomid larvae, zooplankton) p

184 ranges, highlighting the role of mountaintop aquatic invertebrates as sentinels of climate change in

185 ic mercury exposure, MMHg bioaccumulation in aquatic invertebrates did not concomitantly decline.

186 Arctic lakes with greater MMHg in aquatic invertebrates either had (1) higher water MMHg c

187 We exposed the aquatic larvae to the pesticide esfenvalerate (0.11 mug/

188 o Bd during their ontogeny than species with aquatic larvae, and thus they might lack adaptive respon

189 clines of hundreds of amphibian species with aquatic larvae.

190 ced higher mortality rates than species with aquatic larvae.

191 aught amphibian species with terrestrial and aquatic life histories to Bd and found that direct devel

192 udy predicts that many lakes will exceed the aquatic life threshold criterion for chronic chloride ex

193 dated federal criteria for the protection of aquatic life.

194 nt, a desire is that it not adversely affect aquatic life.

195 ers at concentrations considered harmful for aquatic life.

196 organic carbon) previously thought safe for aquatic life.

197 and pollutants with SPM and their impact on aquatic life.

198 study detailing the effects of increasingly aquatic lifestyles on labyrinth morphology among marine

199 est whether these disruptions to terrestrial-aquatic linkages occur during mild summer drought and wh

200 A central paradigm of aquatic locomotion is that cetaceans use fluke strokes t

201 In this study, we examined aquatic macro-invertebrate diversity (family and species

202 to one side of thallus cross sections of the aquatic macrophyte Fucus vesiculosus with laser light sh

203 Absorption profiles of the investigated aquatic macrophyte were different in shape from what is

204 rin polymers (P-CDP) as adsorbents of MPs in aquatic matrixes.

205 ual pesticides or their mixtures can disrupt aquatic microbial communities and there is need to decip

206 In the present study, a laboratory scale aquatic microbial food chain was established using bacte

207 ystem significantly changed the structure of aquatic microbial populations.

208 ls to predict effects on reproduction in the aquatic microcrustacean Daphnia.

209 tle is known about extracellular enzymes and aquatic microorganisms involved in polyester biodegradat

210 on the zebrafish showed that this vertebrate aquatic model also avoids food treated with one of the t

211 Spirodela polyrhiza is a fast-growing aquatic monocot with highly reduced morphology, genome s

212 nge shifts should consider trophic traits of aquatic NIS as these traits are indicative of multiple i

213 and the fish have thus been shown to act as "aquatic noses," supporting a substantial revision of the

214 ction is considered a distance sense; hence, aquatic olfaction is thought to be mediated only by mole

215 larval and adult salamanders with a simple, aquatic-only (paedomorphic) life cycle had an increased

216 hasic lineages, but still 10-fold lower than aquatic-only lineages.

217 ly useful for assessing internal exposure of aquatic organisms across landscapes with differing pH.

218 ticals and personal care products (PPCPs) in aquatic organisms are not well understood.

219 site selection on transcriptomic profiles in aquatic organisms exposed to complex mixtures are lackin

220 vidence of microplastic pollution impacts on aquatic organisms in both marine and freshwater ecosyste

221 and reduced pH, mining activities influence aquatic organisms indirectly through physical alteration

222 whether this pharmaceutical poses a risk to aquatic organisms is debated.

223 estion of microplastic increases exposure of aquatic organisms to hydrophobic contaminants.

224 able chemicals from water and sediments into aquatic organisms under different pH conditions.

225 nto freshwater systems impacts the health of aquatic organisms.

226 (-2) y(-1)), with potential implications for aquatic organisms.

227 terrelationships between abiotic factors and aquatic organisms.

228 nants remain adsorbed following ingestion by aquatic organisms.

229 he environment and subsequent ecotoxicity to aquatic organisms.

230 entified as an additional exposure route for aquatic organisms.

231 aquatic environments and may pose a risk to aquatic organisms.

232 behavior of these contaminants of concern in aquatic organisms.

233 a is a widely distributed species and purely aquatic, our results suggest that persistence and connec

234 whether such influences vary in relation to aquatic oxygen availability.

235 -state species that plays important roles in aquatic photochemical processes.

236 Aquatic photosynthetic organisms cope with low environme

237 We used the decline in aquatic plant richness and cover as an index of ecologic

238 hydr)oxide rind, or Fe plaque, that forms on aquatic plant roots is an important sorbent of metal(loi

239 e sampling approach can be adopted for other aquatic plant systems.

240 eciation and distribution was measured in an aquatic plant, duckweed (Landoltia punctata), exposed to

241 tems, but its influence on interactions with aquatic plants is still unclear.

242 abandoned river channel with open water and aquatic plants; (ii) inundated forest swamp; and (iii) r

243 t of effective risk reduction strategies for aquatic pollutants requires a comprehensive understandin

244 n - a key ecosystem process that can control aquatic productivity - to human land development across

245 We found that CrsR is conserved in many aquatic proteobacteria, and most of the time it is assoc

246 nd this ability is probably widespread among aquatic proteobacteria.

247 Despite their profound adaptations to the aquatic realm and their apparent success throughout the

248 ndustrial importance because of their use in aquatic recreational facilities to remove cyanuric acid,

249 unlikely to be encountered by V. cholerae in aquatic reservoirs or within the human host during infec

250 ociate changes in land cover with downstream aquatic responses.

251 ems from local sources and is transferred to aquatic sedimentary archives on subdecadal to millennial

252 c aromatic hydrocarbons (PAHs), preserved in aquatic sediments from a suburban and a remote catchment

253 Aquatic sediments harbour diverse microbial communities

254 idering the fluxes of metals from and within aquatic sediments, and suggest that other elements' cycl

255 es and we have selected eight representative aquatic species (including tadpoles, fish, water fleas,

256 e toxic effect of a compound over a specific aquatic species as an alternative to get toxicity inform

257 dy is to model chemical products toxicity to aquatic species by means of chromatographic systems to r

258 Direct toxicity measurements using sensitive aquatic species can be carried out but they may become e

259 rice increase; and some high-value declining aquatic species experience severe price increases.

260 an contaminate water and become toxicants to aquatic species or other living beings via the trophic c

261 We find that some aquatic species that school or forage in patchy environm

262 to emulate toxicity in five of the selected aquatic species through some of the chromatographic syst

263 Other aquatic species with similar characteristics to these fi

264 status, distribution, and ecology of alpine aquatic species, particularly in North America, is lacki

265 xa, with lesser attention being dedicated to aquatic species.

266 addressed in adult zebrafish and other small aquatic species.

267 , and contribute to 100 local extinctions of aquatic species.

268 timate factor determining the presence of an aquatic state.

269 l in sustaining phytoplankton growth in many aquatic systems and is pivotal to eutrophication and the

270 While information from aquatic systems and medical microbiology suggests the po

271 e speciation of divalent mercury (Hg(II)) in aquatic systems containing dissolved organic matter (DOM

272 r steady and long-term salinization of these aquatic systems is high.

273 The concentration of CO2 in many aquatic systems is variable, often lower than the KM of

274 re products (HPCPs) and their discharge into aquatic systems means reliable, robust techniques to mon

275 of the total N-nitrosamine pool in technical aquatic systems or biological samples.

276 Glucocorticoids in aquatic systems originating from natural excretion and m

277 ipitates under aerobic conditions in natural aquatic systems scavenges dissolved organic matter (DOM)

278 imes and transitions in both terrestrial and aquatic systems using Fisher information.

279 ctives for surrogation of the eight selected aquatic systems, and thus prediction of toxicity from th

280 igh hardness) are relatively rare in natural aquatic systems.

281 filtration and predator-prey interactions in aquatic systems.

282 useful for the risk assessment of metals in aquatic systems.

283 hydrological and biogeochemical processes in aquatic systems.

284 nvironments such as rain droplets or surface aquatic systems.

285 g to large N losses to the atmosphere and to aquatic systems.

286 on the biology and ecology of basal fungi in aquatic systems.

287 the ecological success of motile bacteria in aquatic systems.

288 More aquatic taxa were recorded in sedDNA, whereas taxa assum

289 mes, as has been observed in terrestrial and aquatic taxa.

290 ication compared to lineages with a complex, aquatic-terrestrial (biphasic) life cycle.

291 context of the vertebrate transition from an aquatic to a terrestrial lifestyle.

292 ee MOA classification methodologies using an aquatic toxicity data set of 3448 chemicals, compare the

293 CAFE contains aquatic toxicity data used in the development of species

294 Enantioselectivity in the aquatic toxicity of chiral pesticides has been widely in

295 ic principle that is likely conserved in all aquatic, undulatory vertebrates.

296 detection frequencies and levels of VMSs in aquatic- versus terrestrial-feeding birds in Canada.

297 Aquatic vertebrates experience strong buoyancy forces th

298 or using LJ001 as a possible therapeutic for aquatic viruses.

299 s in order to fully characterize exposure in aquatic wildlife.

300 hat plastic nanoparticles reduce survival of aquatic zooplankton and penetrate the blood-to-brain bar