ライフサイエンスコーパス: aquatic

1 al ichthyosauriform with the least degree of aquatic adaptation, holding a key to identifying such a

2 Although developed to a lesser degree, aquatic adaptations are also found in other members of t

3 ffinities of mesosaurids, the earliest known aquatic amniotes, which we recover as early diverging pa

4 s assume that arachnids evolved from a fully aquatic ancestor.

5 Aquatic and amphibious mammals face olfactory and thermo

6 among a new subgroup of recently recognized aquatic and bat flaviviruses distinct from the establish

7 We used three closely related aquatic and desert-derived green microalgae in the famil

8 ssion to combat stresses encountered in both aquatic and host environments, including stress posed by

9 ctions underlying holobiont responses across aquatic and terrestrial ecosystems remain largely unreso

10 hotosynthetic organisms that inhabit marine, aquatic and terrestrial ecosystems, diatoms contribute ~

11 As a primary prey source in aquatic and terrestrial ecosystems, these declines will

12 c tons of plastic waste cumulatively entered aquatic and terrestrial ecosystems.

13 In aquatic and terrestrial environments, odorants are dispe

14 a) and assessed the relative contribution of aquatic and terrestrial factors structuring these assemb

15 gonfly communities were associated with both aquatic and terrestrial factors, while diversity was pri

16 Aquatic and terrestrial invertebrates, surface water, se

17 paleobiology remains contentious, with both aquatic and terrestrial lifestyles having been proposed

18 agellates to large mammals belonging to both aquatic and terrestrial realms.

19 rement for the survival of many terrestrial, aquatic, and aerial animal species.

20 ity of D. villosus: Virasure Aquatic, Virkon Aquatic, and Virkon S.

21 raction of pathogens between wild and farmed aquatic animal populations is a concern that remains unc

22 ategy has never been demonstrated in a fully aquatic animal, where sensory cues used for orientation

23 potential to alter microbiome composition of aquatic animals and their vulnerability to disease.

24 Thus, Rhamphorhynchus apparently fed on aquatic animals by grabbing prey whilst flying directly

25 Aquatic animals have developed effective strategies to r

26 ficantly distort visual stimuli presented to aquatic animals in water, yet refraction has often been

27 tion can provide sensory information guiding aquatic animals to key resources or habitats.

28 rough this network.SIGNIFICANCE STATEMENT In aquatic animals, the lateral line is important for detec

29 ions are also known toxicological threats to aquatic animals, we performed a literature search to eva

30 Although aquatic annelid worms have some of the fastest escape re

31 ants (Nepenthes) host diverse communities of aquatic arthropods and microbes in nature.

32 that are key invertebrate predators in both aquatic (as larvae) and terrestrial ecosystems (as adult

33 We profiled (16S rRNA sequencing) > 700 semi-aquatic bacterial communities while measuring their func

34 dietary U uptake, and U elimination for the aquatic baetid mayfly Neocloeon triangulifer.

35 concentrations increased with the degree of aquatic-based diet and at higher trophic levels.

36 eaver Castoroides and estimate the origin of aquatic behavior in beavers to approximately 20 million

37 nt climate adaptation tactics for conserving aquatic biodiversity.

38 ltering the current regime of terrestrial-to-aquatic biogeochemical cycling of C.

39 ed in a wide range of early life stage (ELS) aquatic biota, is a phenomenon by which ultraviolet (UV)

40 eviewed 105 microplastic effect studies with aquatic biota, provided a systematic overview of their c

41 Avian influenza (AI) affects wild aquatic birds and poses hazards to human health, food se

42 isting IAV surveillance data.IMPORTANCE Wild aquatic birds are the primary natural reservoir of influ

43 Wild aquatic birds maintain a large, genetically diverse pool

44 Aquatic birds represent a vast reservoir from which new

45 veral decades of surveillance data from wild aquatic birds sampled along North American migratory fly

46 We found the position of the alula on non-aquatic birds selected for alula optimization to be loca

47 iverse influenza A viruses circulate in wild aquatic birds, occasionally infecting farm animals.

48 Aquatic bladderworts (Utricularia gibba and U. australis

49 hereby defining a form of contact-dependent, aquatic chemosensation.

50 t terrestrial agroecosystem, while nontarget aquatic communities are more sensitive, particularly amo

51 Our results suggest that aquatic communities exhibit a range of responses to clim

52 lity and importance of these proteins in non-aquatic conditions.

53 hwater biodiversity data are unavailable but aquatic connectivity is accounted for, freshwater benefi

54 riability of these pools across the land-sea aquatic continuum.

55 in, we present a surface-anchored artificial aquatic coral polyp composed of a magnetically driven st

56 re elaborated cognitive abilities than their aquatic counterparts such as fish.

57 ular events and adverse outcomes relevant to aquatic ecological risk assessment.

58 ic micropollutants (OMPs) is a challenge for aquatic ecosystem management, and closing the gaps in ri

59 sity of hysteretic responses within a single aquatic ecosystem, and suggest different management stra

60 tion) for the entire complex food web in the aquatic ecosystem.

61 he structure, functions and integrity of the aquatic ecosystem.

62 m Vibrio cholerae is a natural inhabitant of aquatic ecosystems across the planet.

63 ed organic matter plays an important role in aquatic ecosystems and poses a major problem for drinkin

64 tential mercury risk to fish and wildlife in aquatic ecosystems and provides a framework for engaging

65 The ability to transition between aquatic ecosystems and the human host is paramount to th

66 gnificance of PM(1) accumulation by biota in aquatic ecosystems and the potential risk to living orga

67 -term (16-39 years) time series data from 10 aquatic ecosystems and using convergent cross mapping (C

68 acilitate microbial dispersal and affect all aquatic ecosystems has intensified interest in the micro

69 changes in photoreactivity of acid-impacted aquatic ecosystems in response to browning and subsequen

70 P) loading is one of the greatest threats to aquatic ecosystems in the Anthropocene, causing eutrophi

71 r- and polyfluoroalkyl substances (PFASs) in aquatic ecosystems is a global concern because of their

72 -identical core genomes in distant, discrete aquatic ecosystems maintain diversity by possession of n

73 ts or detritus, can trigger abrupt shifts in aquatic ecosystems that may exhibit hysteretic dynamics

74 nobacterial cells and cyanotoxins into SA of aquatic ecosystems which experience HABs.

75 Aquatic ecosystems worldwide face growing threats from e

76 e reduced fish biodiversity and abundance in aquatic ecosystems worldwide(1-3).

77 gies provide measurements of terrestrial and aquatic ecosystems' structure, key for biodiversity stud

78 hotosynthetic microbes that form the base of aquatic ecosystems, and their responses to global change

79 mon first responders to nutrient influxes in aquatic ecosystems, little is known of the sensory mecha

80 zone, the interface between terrestrial and aquatic ecosystems, may decrease anthropogenic nitrogen

81 ssessment of mercury (Hg) bioaccumulation in aquatic ecosystems, using dragonfly larvae as biosentine

82 We assessed the MeE of 305 sites of diverse aquatic ecosystems, worldwide.

83 ive assessment of greenhouse gas emission by aquatic ecosystems.

84 plant and animal remains in terrestrial and aquatic ecosystems.

85 ture affect coupled iron-nutrient cycling in aquatic ecosystems.

86 tic waste generated globally in 2016 entered aquatic ecosystems.

87 stence of potentially hazardous chemicals in aquatic ecosystems.

88 lighting a threat to primary productivity in aquatic ecosystems.

89 mate change stressors across terrestrial and aquatic ecosystems.

90 climate impacts on the temporal stability of aquatic ecosystems.

91 nding these patterns in both terrestrial and aquatic ecosystems.

92 ace organic contaminants could pose risks to aquatic ecosystems.

93 capable of growth and long-term survival in aquatic ecosystems.

94 maintain the integrity and functionality of aquatic ecosystems.

95 n alters the flow of energy and nutrients in aquatic ecosystems.

96 one of the main marine toxins in continental aquatic ecosystems.

97 suggested to provide greatest protection of aquatic ecosystems.

98 an integrated impairment index of Hg risk to aquatic ecosytems and found that 12% of site-years excee

99 an toxicity as well as marine and freshwater aquatic ecotoxicity characterization factors are calcula

100 obal warming will limit the aerobic scope of aquatic ectotherms and may place a greater metabolic bur

101 xygen supply affecting aerobic metabolism of aquatic ectotherms, ecological theories such as the meta

102 ve metabolic rate and hence aerobic scope of aquatic ectotherms.

103 s can propagate to the riparian food web via aquatic emergent insects.

104 ce (P), bioaccumulation (B), mobility in the aquatic environment (M), and toxicity (T) are considered

105 ulation of the mixture of antibiotics on the aquatic environment and human health is urgently needed.

106 Many organic contaminants entering the aquatic environment feature stereogenic structural eleme

107 llution in many countries and to protect the aquatic environment from dye pollution caused by the tex

108 of anthropogenic nanoparticles (NPs) in the aquatic environment has become an emerging concern in te

109 thus, played a role in the formation of the aquatic environment of our planet, making it suitable fo

110 we investigate the occurrence of PAs in the aquatic environment of small Swiss streams combining two

111 he cross-boundary transfer of PFASs from the aquatic environment to the riparian zone via emergent aq

112 of soft stimuli-responsive materials in the aquatic environment would significantly broaden their ap

113 he skull is specialized toward hunting in an aquatic environment, indicated by the placement of the n

114 ponse to the low concentrations found in the aquatic environment, it could mitigate the negative effe

115 itigation of release of antibiotics into the aquatic environment.

116 port and transformation of pollutants in the aquatic environment.

117 one of the most toxic pharmaceuticals in the aquatic environment.

118 herefore be continuously introduced into the aquatic environment.

119 of our time are emerging contaminants in the aquatic environment.

120 nrichment should strongly influence pools of aquatic environmental bacteria, which has the potential

121 icro- and nanoplastics in different types of aquatic environmental media.

122 e major sources of microplastic pollution to aquatic environments and have also been reported in dry

123 mon form of uranium found in terrestrial and aquatic environments and is a central component in nucle

124 associated with vertebrate's adaptations to aquatic environments and other environmental changes.

125 The samples were derived from different aquatic environments but close relatives could be isolat

126 s(14), pointing to a substantial invasion of aquatic environments by dinosaurs.

127 olved organic matter (DOM) across a range of aquatic environments highlighting the role of DOM in glo

128 hropogenic Hg from terrestrial landscapes to aquatic environments in the region, potentially leading

129 and limnic waters has redefined the role of aquatic environments in the regional CH(4) cycle.

130 Pesticides commonly contaminate the aquatic environments inhabited by mosquito juveniles.

131 RNA viruses in aquatic environments remain poorly studied.

132 f microplastics in the surface microlayer of aquatic environments using glass plate dipping holds pro

133 , such as sauropods and hadrosaurs, lived in aquatic environments(2,3) were abandoned decades ago(4-6

134 ly affiliated to ubiquitous (terrestrial and aquatic environments) taxa.

135 It is hypothesized that to cope with aquatic environments, amphibious mammals have expanded t

136 In aquatic environments, species might not be able to redis

137 In aquatic environments, V. cholerae exists both as plankto

138 These worms live in aquatic environments, where they are likely to encounter

139 Faced with limited access to CO(2) in aquatic environments, which can vary daily or hourly, th

140 ften similarly persistent but more mobile in aquatic environments, which implies an increasing exposu

141 ins in cultivated bacteria isolated from non-aquatic environments.

142 l for species and biodiversity monitoring in aquatic environments.

143 ioavailable sediment-associated chemicals in aquatic environments.

144 fe of secondary plastid-bearing organisms in aquatic environments.

145 sosaurs were the first amniotes to re-invade aquatic environments.

146 selection for, and human exposure to, AMR in aquatic environments.

147 harbouring rhodopsins are isolated from non-aquatic environments.

148 mergent macrophytes on nutrient retention in aquatic environments.

149 ecosystem engineers and keystone species in aquatic environments.

150 -driven species distributions in forests and aquatic environments.

151 neered nanoparticle (ENP), could be found in aquatic environments.

152 unity included canopy cover and slope, while aquatic factors included water temperature, dissolved ox

153 giosperms and Marsileaceae, a family of semi-aquatic ferns that are among the only land plants to mat

154 ergent adaptive landscapes are recovered for aquatic fishes and terrestrial crown tetrapods, each of

155 or the first time, in vivo replication of an aquatic flavivirus was demonstrated following intracoelo

156 to an expanding group of recently discovered aquatic flaviviruses.

157 l will allow SFV to serve as a prototype for aquatic flaviviruses.

158 between air and water and chord angle during aquatic flight, expanding their performance envelope.

159 mate aggregate global human, terrestrial and aquatic food animal antimicrobial use in 2030 at 236,757

160 ASs was the major pathway of exposure in the aquatic food web and bioaccumulation in the riparian foo

161 and protozoans and a basal resource for the aquatic food web, showed high PFAS accumulation (in 10 o

162 global carbon fixation, they underpin major aquatic food webs and drive global biogeochemical cycles

163 ffective indicators of Hg bioavailability in aquatic food webs.

164 s Hg bioaccumulation and biomagnification in aquatic food webs; and (3) Se inhibits Hg bioavailabilit

165 ibility of affordable and sustainable farmed aquatic foods should focus on freshwater aquaculture.

166 Surprisingly, we find an absence of aquatic foods, including in ceramics from coastal sites,

167 ion to the bio-geochemical Fe redox cycle in aquatic freshwater sediments.

168 f organic matter, and sampled communities of aquatic fungi and benthic invertebrates.

169 iparian habitat protection while maintaining aquatic habitat and habitat quality.

170 y among distributed wetlands is critical for aquatic habitat integrity and to maintain metapopulation

171 c wetlands, provided a range of riparian and aquatic habitat variability ideal for studying dragonfly

172 colonizing every conceivable terrestrial and aquatic habitat, only five Halobates (Heteroptera: Gerri

173 , and limitations to inorganic carbon in the aquatic habitat, whereas Rubisco in extant land plants r

174 d to tires, traditionally know as productive aquatic habitats for Ae. aegypti.

175 lls to determine what are the most important aquatic habitats in the proliferation of Ae. aegypti in

176 Moreover, by targeting the most productive aquatic habitats this approach will allow the developmen

177 rvae and pupae count data, type and count of aquatic habitats, and daily rainfall.

178 trol response efforts to the most productive aquatic habitats.

179 Despite the fully aquatic habits of cetaceans, immunologic exposure to arb

180 ted to exceed the 15 mug L(-1) threshold for aquatic health in most rivers.

181 Together, these results suggest that aquatic insect body size is an important predictor of su

182 d Sigma(24)PFAS concentrations were found in aquatic insect larvae, such as dragon- and damselflies,

183 est a trophic link between biofilm PFASs and aquatic insect PFASs.

184 ts; all 14 PFASs were detected in individual aquatic insect samples (range of <limit of detection [<L

185 tly and positively related to mining extent, aquatic insect Se flux was not associated with mining ex

186 he effects of transient thermal stress in an aquatic insect, we first identified static temperatures

187 llenges of climate change for high-elevation aquatic insects and how they may respond, focusing on cu

188 Aquatic insects are vital to stream ecosystem function a

189 Adult aquatic insects can be important vectors of waterborne c

190 We show that high-elevation aquatic insects may not be physiologically threatened by

191 nted rate, it is imperative that we know how aquatic insects respond to increasing temperature and wh

192 onstrated strong size-dependent responses of aquatic insects to metals.

193 aqueous metal toxicity generally demonstrate aquatic insects tolerate relatively high concentrations

194 Even though Se concentrations in aquatic insects were significantly and positively relate

195 nvironment to the riparian zone via emergent aquatic insects.

196 y unknown effects on resident communities of aquatic insects.

197 erning the bioaccumulation of uranium (U) in aquatic insects.

198 ons and greatest concentrations of PFASs was aquatic insects; all 14 PFASs were detected in individua

199 mmercial shipping is a prominent pathway for aquatic invasions.

200 a point where they can be widely applied to aquatic invasive species management.

201 estions by reviewing published literature on aquatic invertebrate communities from stream ecosystems.

202 individual-based culture experiments on the aquatic invertebrate, Brachionus manjavacas (Rotifera).

203 easure the sensitivity (EC(50)-values) of 10 aquatic invertebrates toward a 24 h pulse of the pyrethr

204 dure is applied to twelve species of diverse aquatic invertebrates, including both pelagic and benthi

205 Soft-bodied aquatic invertebrates, such as sea slugs and snails, are

206 ation potential and toxicity in two keystone aquatic invertebrates: Gammarus pulex and Hyalella aztec

207 the safeguarding of human health, animal and aquatic life, and the environment.

208 have been created to regulate it and protect aquatic life.

209 sistent with the suite of adaptations for an aquatic lifestyle and piscivorous diet that have previou

210 Recapitulation of such multimodal aquatic locomotion in small-scale soft robots is challen

211 llustrate the transition from semiaquatic to aquatic locomotion, including development of a fusiform

212 sosaurs has important implications for their aquatic locomotion.

213 e of environmental DNA (eDNA) for monitoring aquatic macrofauna allows the non-invasive species deter

214 To do so, we contrasted aquatic-macroinvertebrate assemblage structure (family l

215 Between 2011 and 2016, aquatic macroinvertebrates were sampled across a gradien

216 nd similarities and differences between this aquatic mammal and terrestrial mammals.

217 t evidence of direct interactions between an aquatic mammal, the West Indian manatee, a federally thr

218 ical, such as during unihemispheric sleep in aquatic mammals (cetaceans, sirens, and Otariid seals).

219 to variations in photosynthetic activity of aquatic micro-organisms is crucially important for under

220 Vibrio cholerae is an aquatic microbe that can be divided into three subtypes:

221 Magnetotactic bacteria (MTB) are ubiquitous aquatic microorganisms that mineralize dissolved iron in

222 n of fluoxetine in the zebrafish embryo - an aquatic model organism of intermediate complexity.

223 , mirroring the diversity of terrestrial and aquatic niches where plant and/or algal cellulosic cell

224 ticides are known to be highly toxic to most aquatic nontarget organisms, but little is known about t

225 expressed specifically in breathing gills of aquatic nymphs, suggesting a novel sensory role for this

226 Aromatic amines are relevant aquatic organic contaminants whose photochemical transfo

227 ic rates (i.e., oxygen consumption rates) of aquatic organisms and restricts predictions to resting m

228 t combinations of chemical stressors because aquatic organisms are exposed to several natural and art

229 be a novel tool to help identify areas where aquatic organisms are impacted by oil and gas produced w

230 Although adverse effects of AgNPs on aquatic organisms have been extensively studied, there i

231 In aquatic organisms such as zebrafish, osmotic shock follo

232 ss, ecological niches, and responses of many aquatic organisms to climate change.

233 mixture exposure conditions that may impact aquatic organisms via drug-drug interactions.

234 accumulate pesticides and may be consumed by aquatic organisms.

235 between nutrient enrichment and diseases of aquatic organisms.

236 d has substantial ecotoxicity, especially to aquatic organisms.

237 s constrain the habitable environment of all aquatic organisms.

238 on the maternal and subsequent generation of aquatic organisms.

239 of Al on human health, water treatment, and aquatic organisms.

240 watersheds, water quality, and the health of aquatic organisms.

241 any pollutants cause endocrine disruption in aquatic organisms.

242 plants (WWTPs), poses a potential threat for aquatic organisms.

243 omega-3 fatty acid, were the major PUFAs in aquatic origin lecithins (RL and WL).

244 When plants emerged from their aquatic origins to colonise land, they needed to avoid d

245 The dispersal ability of aquatic parasites with complex life cycles differs stron

246 e when foraging, making them the first fully aquatic path-integrating animals yet discovered.

247 on ponds by integrating solar irradiance and aquatic photochemistry models under uncertainty.

248 The 'Aquatic picorna-like viruses/Marnaviridae' clade was gre

249 acred lotus (Nelumbo nucifera) is an ancient aquatic plant of medicinal value because of antiviral an

250 l questions regarding the biogeochemistry of aquatic plant roots.

251 o globally distributed, ecologically similar aquatic plant species.

252 s from aquaculture (excluding the farming of aquatic plants), with a focus on using modern, commercia

253 osystem populated by groundwater-fed rivers, aquatic plants, angiosperm shrublands, and edible plants

254 The roots of aquatic plants, including rice, release oxygen into the

255 is an environmentally harmful and ubiquitous aquatic pollutant with extensive production and applicat

256 otope composition of diatoms, which dominate aquatic primary productivity.

257 Here we present unambiguous evidence for an aquatic propulsive structure in a dinosaur, the giant th

258 mall foraging in 74 well-resolved (primarily aquatic) real-world food webs.

259 nce of the tail for propulsion in many other aquatic reptiles, the identification of fracture planes

260 While prior studies have shown that aquatic reservoirs are important in the persistence of t

261 show robust evidence of the establishment of aquatic reservoirs as well as ongoing evolution of V. ch

262 ere for large surplus capture and storage of aquatic resources that were controlled and managed by co

263 During her short life, she ate aquatic resources, and is related to ancient Beringian a

264 of the subsistence systems and the role that aquatic resources, terrestrial mammalian game, and plant

265 trial mammals and variably complemented with aquatic resources.

266 iscerning the composition of soil, plant and aquatic samples containing complex mixtures of proteins,

267 antially lower than those measured for other aquatic samples.

268 redox cycling in the oxic and photic zone of aquatic sediments.

269 e production of dissolved Fe(II) (Fe(2+)) in aquatic sediments.

270 habitats of magnetotactic bacteria, such as aquatic sediments.

271 going evolution of V. cholerae isolates from aquatic sites.

272 However, this expansion toward aquatic soft robots is hampered by the slow response of

273 ing amoebae (FLA) are ubiquitous protozoa in aquatic/soil habitats and known to resist various disinf

274 ponse across time and space, suggesting that aquatic species adjusted in a variety of habitats to sup

275 anticipated risks of 6PPD antioxidants to an aquatic species and imply toxicological relevance for di

276 y genome assemblies and annotations for many aquatic species still presents significant challenges du

277 markedly influenced by its own metabolism in aquatic species, this study investigated the biotransfor

278 logical reductions seen among highly adapted aquatic species.

279 pplies the oldest compelling evidence for an aquatic stem group for either Myriapoda or Hexapoda, pre

280 ained by volatilization from terrestrial and aquatic surfaces and supplemented with human activities

281 duction and soil respiration) is exported to aquatic systems as leached DOC.

282 elated to mining are thus not constrained to aquatic systems but extend to terrestrial habitats and f

283 , potentially intensifying eutrophication in aquatic systems, for example, the increased persistence

284 for DMHg, and a potential source of MMHg, in aquatic systems.

285 vironmental parameters influence ENM fate in aquatic systems.

286 pathway for sunlight-absorbing compounds in aquatic systems.

287 hods used for emerging contaminants (ECs) in aquatic systems.

288 ved inorganic phosphorus (DIP) is low in the aquatic systems.

289 ly result in higher methylation rates at the aquatic-terrestrial interface and more efficient downstr

290 In aquatic testing and research of such mixtures, it is cha

291 rol mixture concentration and composition in aquatic tests, and (iii) discussing the fundamental diff

292 ians are a cosmopolitan clade of secondarily aquatic tetrapods that inhabited low-latitude, nearshore

293 DPs apparently began to emerge during the aquatic-to-land transition, with phylogenetic analyses r

294 ated the phylogeography of both clinical and aquatic toxigenic V. cholerae O1 isolates and show robus

295 Here, we focus on viruses of aquatic unicellular organisms, which exhibit the greates

296 osystem productivity on Earth's most diverse aquatic vertebrate fauna and highlights the importance o

297 mance are more comparable to those of extant aquatic vertebrates that use vertically expanded tails t

298 function in chondrichthyan fishes and other aquatic vertebrates.

299 to cause mortality of D. villosus: Virasure Aquatic, Virkon Aquatic, and Virkon S.

300 ally intensifying anthropogenic pressures on aquatic wildlife habitats.