ライフサイエンスコーパス: freshwater

1 ted with additional aspects of adaptation to freshwater.

2 and the influence of the lower delta(18)O of freshwater.

3 pine stickleback (Gasterosteus aculeatus) to freshwater.

4 based water quality criteria (WQC) for Cu in freshwater.

5 all of which may influence eutrophication of freshwaters.

6 the range of 2.8-280 days in typical sunlit freshwaters.

7 t this coupling has not been investigated in freshwaters.

8 ility of previously frozen solutes to Arctic freshwaters.

9 To investigate how freshwater algal production in the Eel River, northern C

10 Managing freshwater allocation for a highly populated and growing

11 veloped an individual-based model (IBM) of a freshwater amphipod detritivore, Gammarus pseudolimnaeus

12 er, and the most common examples of these in freshwater and coastal seawater are fulvic and humic aci

13 Freshwater and its macrophytes had higher N and P concen

14 o protect significant swaths of terrestrial, freshwater and marine ecosystems from a range of threats

15 ecological consequences across terrestrial, freshwater and marine ecosystems.

16 ses in primary producers at the base of both freshwater and marine ecosystems.

17 Cladoceromorpha), which live in all kinds of freshwater and occasionally marine environments [1, 2].

18 ankton has previously been evaluated only in freshwater and regional seas, but not for the large olig

19 nto the marine plankton, the colonization of freshwater and semiterrestrial environments, and the evo

20 gut signals were detectable over background freshwater and soil/runoff related signals, even at tens

21 ons to exceed the minimum toxic threshold in freshwater and some soils, though this is more likely wi

22 e characterization of suspended particles in freshwater and the dissolution rate of ENPs are two sign

23 ised coastal subterranean habitats or nearby freshwaters and have a highly disconnected distribution

24 and associated chloride runoff can salinize freshwaters and threaten lake water quality and the many

25 depths, habitat features (i.e., brackish vs. freshwaters), and nucleic acids (DNA vs. RNA), suggestin

26 ons of 100 of the most invasive terrestrial, freshwater, and marine species in Europe.

27 vidence that at least 31 lineages of marine, freshwater, and terrestrial crustaceans (including 64 fa

28 Marine, freshwater, and terrestrial species are all widespread,

29 Hydra, a simple freshwater animal famous for its regenerative capabiliti

30 ing strategies employed by a metal-tolerant, freshwater animal in a field situation.

31 ite-specific water demands to indicate where freshwater appropriation might pose high socioenvironmen

32 Nutrient concentrations in freshwater are highly variable over time, with changes d

33 ssential ecosystem service, but catches from freshwaters are often overlooked.

34 raits that underpin ecological adaptation of freshwater bacteria to lake habitats can be phylogenetic

35 variation in the range size distributions of freshwater bacteria, a trend which may be determined, in

36 ted understanding of how these events affect freshwater bacterial communities.

37 We found that the freshwater bacterial community associated with cyanobact

38 siphoviruses, CbK-like phages, which infect freshwater bacterium Caulobacter crescentus.

39 matium oxaliferum, the world's biggest known freshwater bacterium, harbor genetic diversity typical o

40 describe a cooperative modeling approach for freshwater beaches impacted by point sources in which in

41 evaluated swimming and wading in marine and freshwater beaches in six U.S. states, and CHEERS, which

42 n the potential impacts of climate change on freshwater biodiversity at scales that inform management

43 ronmental regulators to conserve and enhance freshwater biodiversity in urbanized landscapes whilst a

44 Effective conservation of freshwater biodiversity requires spatially explicit inve

45 eed to be taken to ensure the persistence of freshwater biodiversity under climate change.

46 nts, were determined in sediment, water, and freshwater biota in an urban creek in Canada.

47 yrus milloti is an irreplaceable link to the freshwater biota of the Mesozoic and serves as a reminde

48 tential impacts of changes to pCO2 levels on freshwater biota.

49 Results of this study show the importance of freshwater bivalves for improving water quality through

50 king and sampling study showed filtration by freshwater bivalves resulting in 1-1.5 log10 reduction o

51 icaudata), which typically inhabit temporary freshwater bodies, and water fleas (Cladoceromorpha), wh

52 salmonae, has a complex lifecycle exploiting freshwater bryozoans as primary hosts and salmonids as s

53 integrated assessment, to our knowledge, of freshwater carbon fluxes for the conterminous United Sta

54 Seventeen freshwater CFs of nano-Cu are proposed as recommended va

55 ive mass recession was most prevalent at our freshwater colony, being detected among 34-38% of chicks

56 port of organic and inorganic materials, and freshwater community structure and function.

57 We demonstrate that, relative to freshwater conditions, seawater halides can increase pho

58 We also assessed the life cycle freshwater consumptions of Bakken-derived gasoline and d

59 m the skin of beluga sturgeon (Huso huso) on freshwater crayfish (Astacus leptodactylus) muscle subje

60 This study demonstrates the potential to use freshwater crayfish as a benthic-zone indicator of nanos

61 al elemental distribution profile within the freshwater crustacean Ceriodaphnia dubia was constructed

62 FPW toxicity to the model freshwater crustacean Daphnia magna was characterized ut

63 We test this hypothesis with the freshwater crustacean Gammarus pulex and four toxicants

64 his lattice in beta-type carboxysomes of the freshwater cyanobacterium Synechococcus elongatus, CcmM,

65 The three inland, freshwater datasets are ELA, TROUT and SWAT.

66 accumulation from waterborne cadmium by the freshwater decapod crustacean Macrobrachium australiense

67 ofossil analyses indicate that predominantly freshwater deposits bury relic intertidal deposits at th

68 Abundances of freshwater diatom frustules exported to Eel Canyon sedim

69 e quantified siliceous shells (frustules) of freshwater diatoms from a well-dated undisturbed sedimen

70 ne and less saline fluids related to onshore freshwater discharge at sea through a sealed water-table

71 Our model response to freshwater discharge coming from Greenland melting revea

72 The ensuing freshwater discharge coming from ice sheets could have s

73 Nearly half of the freshwater discharge into the Gulf of Alaska originates

74 of massive iceberg surges, leading to large freshwater discharges.

75 aters with millimolar sodium chloride level (freshwater, drinking water, and aquarium water, as well

76 ngs, much of the TC flood losses are instead freshwater-driven, often extending far inland from the l

77 d identifies policy deficiencies that hinder freshwater ecosystem protection.

78 le towards preventing further degradation of freshwater ecosystems and maintaining connectivity among

79 ates the structure and function of Amazonian freshwater ecosystems and the provisioning of services t

80 Freshwater ecosystems are exposed to many stressors, inc

81 Nutrients in freshwater ecosystems are highly variable in space and t

82 laid to assess the vulnerability of European freshwater ecosystems at the catchment scale (18 783 cat

83 This degradation of Amazonian freshwater ecosystems cannot be curbed presently because

84 acts on aquatic organisms in both marine and freshwater ecosystems highlights a pressing need for ade

85 xtreme changes have amplified threats to the freshwater ecosystems that dominate the landscape in man

86 n is an important food source at the base of freshwater ecosystems that tends to bioconcentrate trace

87 N and P concentrations in freshwater ecosystems were positively correlated and N :

88 drological alterations are rapidly degrading freshwater ecosystems, both independently and via comple

89 n (N):phosphorus (P) stoichiometry in global freshwater ecosystems, but this is not yet well-assessed

90 diversity, and impact of anammox bacteria in freshwater ecosystems, however, is largely unknown, conf

91 xamined these impacts in Arctic or Subarctic freshwater ecosystems, where the climate is changing mos

92 r accumulation of P than N in human-impacted freshwater ecosystems, which could have large effects on

93 xpected to exacerbate the current threats to freshwater ecosystems, yet multifaceted studies on the p

94 is a major driver causing declines of global freshwater ecosystems, yet the ecological consequences f

95 ing climate change vulnerability tailored to freshwater ecosystems.

96 ses of selenium-laden waste streams threaten freshwater ecosystems.

97 Hg concentrations, contrasting findings from freshwater ecosystems.

98 e using some of the best routinely monitored freshwater ecosystems.

99 l climate change (GCC) can negatively affect freshwater ecosystems.

100 nd overlook the hydrological connectivity of freshwater ecosystems.

101 lasses and OTUs frequently detected in other freshwater ecosystems.

102 itoring approach is relatively unexplored in freshwater ecosystems.

103 arming and associated accelerated drying for freshwater ecosystems.

104 r, water, and soil emission compartments for freshwater ecotoxicity and human toxicity, both cancer e

105 Here, using a freshwater enrichment culture, we show that archaea of t

106 ion was higher in the marine compared to the freshwater environment, explained by the cumulative hist

107 n stable against self-aggregation in typical freshwater environments and in neutral cloud droplets bu

108 ere a biological vector transporting Hg from freshwater environments into marine ecosystems.

109 bacterial arborinol producers in marine and freshwater environments that could expand our understand

110 e high flow winter samples resembled more to freshwater environments while samples during the decreas

111 cultatively anaerobic bacteria from soil and freshwater environments.

112 rtitioning behaviors of SDPAs and BZT-UVs in freshwater environments.

113 and causing acidification of both marine and freshwater environments.

114 tion in future models of microcystin fate in freshwater-estuarine systems.

115 for ENPs has been developed to calculate the freshwater fate factor (FF) of ENPs.

116 stock recovery of the world's largest scaled freshwater fish (Arapaima gigas), providing both food an

117 red in the distal digesta of Atlantic salmon freshwater fish (FW) kept in a commercial Scottish fresh

118 imit of detection of 0.08 mg N-TMA kg(-1) in freshwater fish and 1 mg N-TMA kg(-1) in marine fish.

119 find that for those consuming locally caught freshwater fish from the United States, rather than mari

120 s of B. rousseauxii are the longest strictly freshwater fish migrations in the world.

121 Low concentrations of REE in freshwater fish muscle compared to their potential inver

122 iologically linked to the consumption of raw freshwater fish occurred in Singapore.

123 re likely to provide a good approximation of freshwater fish sensitivity to climate change, disentang

124 review, we investigated this question in 82 freshwater fish species (27 families) representing 829 e

125 By characterizing genetic structure in a freshwater fish species (Hollandichthys multifasciatus)

126 effective on field samples from two benthic freshwater fish species, revealing a microplastic burden

127 understanding the high species diversity of freshwater fish that we currently observe in the world,

128 etermine the toxic mechanism(s) of HF-FPW on freshwater fish, and aid in establishing monitoring, tre

129 a zoonotic GBS clone associated with farmed freshwater fish, capable of causing severe disease in hu

130 Sustainable management of freshwater fisheries and biodiversity requires accountin

131 lse that predict yield in one of the largest freshwater fisheries in the world.

132 eographic footprint of nutrient excretion by freshwater fishes across the United States and reveal di

133 Here, we examine the response of freshwater fishes and their nutrient excretion - a key e

134 us studies, suggest that Hg trends in Arctic freshwater fishes before 2001 were spatially and tempora

135 lp assess one-third (ca 4000 species) of all freshwater fishes in need of assessment by 2020.

136 nce past extirpation probabilities of native freshwater fishes in the Upper and Lower Colorado River

137 We focus on freshwater fishes, which constitute a significant portio

138 In this study, we reacted freshwater flocs (704-1280 mg As/kg) from a minerotrophi

139 uilibria (e.g., in stagnant waters), Fe-rich freshwater flocs are expected to remain an effective sin

140 anic matter (OM)-rich (18.1 and 21.8 wt % C) freshwater flocs dominated by ferrihydrite and nanocryst

141 to assess the potential future changes in TC freshwater flood risk due to changing climate pattern an

142 st time a comprehensive assessment of the TC freshwater flood risk from the full set of all significa

143 Despite this actuality, knowledge of TC freshwater flood risk is still limited.

144 We find that the areas impacted by freshwater flooding are nearly equally divided between c

145 ity and more frequent and severe extremes in freshwater flow.

146 ta to downstream ecosystems will increase as freshwater flux from the GrIS rises in a warming world.

147 rth Atlantic; however, whether the augmented freshwater flux is disrupting the AMOC is unclear.

148 the mid-1990s, making the connection to the freshwater flux unclear.

149 e mainly influenced by the anomalous surface freshwater flux.

150 Delta Estuary watershed is a major source of freshwater for California and a profoundly human-impacte

151 projected reductions in the availability of freshwater for irrigation in India.

152 The availability of freshwater for irrigation in the Indian agricultural sec

153 suggest that, in response to North Atlantic freshwater forcing during the early phase of the last de

154 er storm track in response to North Atlantic freshwater forcing, a mechanism suggested by simulations

155 e focus on its effects on coastal islands of freshwater forest in Florida's Big Bend region, extendin

156 mited freshwater systems and therefore place freshwater functions and attendant ecosystem services at

157 The system can be used to study freshwater gill physiology, and it is a humane alternati

158 ption that the behaviour of these late-stage freshwater glass eels, and their responses to magnetic f

159 gae, and the Streptophyta, which consists of freshwater green algae and the land plants.

160 Sargasso Sea breeding grounds to coastal and freshwater habitats from North Africa to Scandinavia [6,

161 mals than in plants (50% versus 39%), and in freshwater habitats relative to terrestrial and marine h

162 egarding the consequences of urbanization on freshwater habitats, especially small lentic systems.

163 ysis of studies conducted in both marine and freshwater habitats.

164 aerosol (LSA) produced from wave-breaking in freshwater HABs.

165 ater fish (FW) kept in a commercial Scottish freshwater hatchery with that of their full-siblings aft

166 Aerosols from freshwater have the potential to impact regional climate

167 ecords, the authors show that Southern Ocean freshwater hosing can trigger global change.

168 symmetric extratropical forcings (icesheets, freshwater hosing) generally produce meridional shifts i

169 ndings provide new insights into the role of freshwaters in global C and Si biogeochemical cycles.

170 Freshwater inland wetlands, in part due to their substan

171 ospheric circulation occurred in response to freshwater input and associated cooling in the North Atl

172 changes in NADW or AABW properties caused by freshwater input as suggested previously, the observed p

173 il its complete infilling few centuries ago, freshwater input from the Indus, and perhaps from the Gh

174 ed by climate-scale models as a near-surface freshwater input to the ocean, yet measurements around A

175 Terrestrial freshwater inputs to coastal sediments were identified a

176 hydrology (e.g., precipitation/evaporation, freshwater inputs) and global ice volume.

177 cate seminatural populations of a coevolving freshwater invertebrate-parasite system (host: Daphnia m

178 The ingestion of microplastics by freshwater invertebrates has not been reported outside t

179 dissociation of Pu-NOM complexes in natural freshwaters is currently unknown.

180 oach for the analysis of dissolved lignin in freshwaters is presented.

181 ultured and uncultured MTB from brackish and freshwater lagoons were studied using analytical transmi

182 s in Lake Superior, which is Earth's largest freshwater lake by area, are not well documented (spatia

183 on in Yellowstone Lake and likely other oxic freshwater lake environments, and that Pseudomonas sp. p

184 A comparison of bromeliads to freshwater lake sediments and soil from around the world

185 y of anammox bacteria in the world's largest freshwater lake-Lake Superior.

186 Cyanobacterial blooms often occur in freshwater lakes and constitute a potential health risk

187 In freshwater lakes, harmful algal blooms (HABs) of Cyanoba

188 Freshwater lakes, in turn, have a disproportionate influ

189 Aerosol production from wave breaking on freshwater lakes, including the Laurentian Great Lakes,

190 gae are becoming larger and more frequent in freshwater lakes.

191 heir putative ecological interactions in two freshwater lakes.

192 near-complete genomes, in two North American freshwater lakes.

193 ined pelagic methane enriched zone (PMEZ) in freshwater lakes.

194 ater and solutes enter and propagate through freshwater landscapes in the Anthropocene is critical to

195 cal cycles of estuaries and coastal areas by freshwater loadings, and reinforce the importance of reh

196 rococci was measured at multiple depths in a freshwater marsh, a brackish water lagoon, and a marine

197 Using Sumatran freshwater mayfly communities, we test whether elevation

198 hance current efforts to monitor and protect freshwater mussel biodiversity.

199 both the presence/absence and abundance of a freshwater mussel species, Lampsilis siliquoidea.

200 mtDNA transmission widespread in gonochoric freshwater mussels (Bivalvia: Palaeoheterodonta: Unionid

201 Freshwater mussels are vital components of stream ecosys

202 ecay rates reported within are the first for freshwater mussels.

203 cent laboratory study of bioturbation by the freshwater oligochaete worm Lumbriculus variegatus, and

204 gricultural lands receiving biosolids and in freshwater or marine sediments.

205 The long-term effects of oil spills on freshwater organisms have been little studied.

206 Holocene climate is potentially dominated by freshwater outburst events, whilst ~1500 year cycles in

207 The increased freshwater output from Antarctica is important in determ

208 in and gaining a better understanding of how freshwater pCO2 levels are regulated and how these level

209 g atmospheric CO2 may also indirectly impact freshwater pCO2 levels in a variety of systems by affect

210 els of atmospheric CO2 may directly increase freshwater pCO2 levels in lakes, but rising atmospheric

211 Although future freshwater pCO2 levels remain uncertain, studies have co

212 Freshwater pCO2 varies across systems and is controlled

213 Freshwater peatlands are carbon accumulating ecosystems

214 sed to differentiate peptide dynamics in the freshwater planarian flatwormSchmidtea mediterraneaat di

215 The asexual freshwater planarian is a constitutive adult, whose cent

216 Here we identify two boule paralogs in the freshwater planarian Schmidtea mediterranea Smed-boule1

217 and porphyrin-producing cells in the brown, freshwater planarian Schmidtea mediterranea Using an RNA

218 Asexual freshwater planarians reproduce by tearing themselves in

219 However, the degree to which freshwater populations can acclimate to long-term warmin

220 t copy number differences between marine and freshwater populations.

221 White tail disease in the giant freshwater prawn Macrobrachium rosenbergii causes signif

222 a highly degraded incised stream affects the freshwater production of steelhead (Oncorhynchus mykiss)

223 '-Polui demonstrate that both were consuming freshwater protein; indicating that the humans were feed

224 model, 13 input parameters (such as depth of freshwater, radius of ENPs) show vastly different degree

225 short memory of the tidal signal when inland freshwater recharge was large.

226 More than 97% of the world's freshwater reserves are found in aquifers, making ground

227 tiest rivers by annual flows, supplies vital freshwater resources to populous downstream locations, a

228 he potential to alter many facets of Earth's freshwater resources, especially lacustrine ecosystems.

229 Affluence, not the availability of freshwater resources, was found to be the most critical

230 (NPR) is one option for conserving valuable freshwater resources.

231 ve irrigation sources for areas with limited freshwater resources.

232 , herbivory, and organic matter quality in a freshwater river network.

233 increasing ice mass loss and the associated freshwater runoff and lengthening of open-water periods.

234 air temperatures above 0 degrees C per year, freshwater runoff and sea ice in the 1980s) rather than

235 unaffected by human activity, but increased freshwater runoff and sediment fluxes may increase the s

236 d that delta progradation was driven by high freshwater runoff from the Greenland Ice Sheet coincidin

237 derstanding of how climate-driven changes in freshwater runoff have the potential to alter food web d

238 and wild felids, are carried to the ocean by freshwater runoff.

239 ity divided statistically into three groups: freshwater (salinity < 0.5 per thousand), oligohaline an

240 dy, LSA were produced in the laboratory from freshwater samples collected from Lake Michigan and Lake

241 Freshwater sediment slurries were incubated anaerobicall

242 mproved understanding of nitrogen cycling in freshwater sediments.

243 ed by initial deposition of this facies in a freshwater setting.

244 ulture science can offer for both marine and freshwater settings.

245 The availability of plants and freshwater shapes the diets and social behavior of chimp

246 The evolutionary history of the old, diverse freshwater shrimp genus Caridina is still poorly underst

247 These records reveal a clear HS11 freshwater signal, which attenuated toward the eMed, and

248 ically impoverished asexual populations of a freshwater snail, Potamopyrgus antipodarum, from distinc

249 ude values were, in fact, taken from inland, freshwater sources.

250 l controls of U bioavailability in the model freshwater species Lymnaea stagnalis (Gastropoda).

251 Our vulnerability framework includes 1685 freshwater species of plants, fishes, molluscs, odonates

252 volved from marine populations, we show that freshwater stickleback also act as reservoirs for ancien

253 Although freshwater stickleback have repeatedly evolved from mari

254 s resulting from ice melting and terrestrial freshwater storage and allows for the identification of

255 Unlike freshwater strains, membranes are almost devoid of C18,

256 Field deployment of Cu-based NP samples in a freshwater stream confirmed these conclusions for a natu

257 cy that promotes expansion of unconventional freshwater supply options, such as wastewater recycling

258 pproaches for Saudi Arabia's electricity and freshwater supply systems.

259 s consume more electricity than conventional freshwater supply technologies, Saudi Arabia's electrici

260 del experiments using HadCM3 with an imposed freshwater surface "hosing" to simulate glacial lake dra

261 New approaches to freshwater sustainability - implemented through scientif

262 The freshwater swimming pools of the Cavu River harbour many

263 ed delta(18)ONO3 vs. delta(15)NNO3 trends in freshwater systems (<1) must result from concurrent NO3(

264 to monitor inorganic nutrients in different freshwater systems (i.e., streams and wetlands) with a r

265 wide do not adequately protect their limited freshwater systems and therefore place freshwater functi

266 Natural freshwater systems have been severely affected by excess

267 cals and personal care products (PPCPs) into freshwater systems impacts the health of aquatic organis

268 onmental forcing, as well as re-invasions of freshwater systems on continental basins by multiple lin

269 changed dramatically in most of the studied freshwater systems over short time scales, while there w

270 daptive management - are required to protect freshwater systems through periods of changing societal

271 ic evidence compels enhanced protections for freshwater systems, especially for impermanent streams a

272 n to reduce methane emissions by over 50% in freshwater systems, its main natural contributor to the

273 ncentrations and trophic patterns for REE in freshwater temperate lakes in Quebec, Canada.

274 into rivers are benthic and fully adapted to freshwater; that is, they are late-stage glass eels ( ap

275 of acid rain have acidified forest soils and freshwaters throughout montane forests of the northeaste

276 as found in estuarine emergent wetlands with freshwater tidal wetlands holding about 19%.

277 trichs may have transitioned repeatedly from freshwater to brackish/marine/hypersaline environments.

278 e migration of anadromous fish from low-food freshwater to high-food marine environments.

279 ing the transfer of biological material from freshwater to the atmosphere via LSA is crucial for dete

280 c physiological changes as they migrate from freshwater to the marine environment.

281 that use of the low-herbicide regime reduced freshwater toxicity loads by 81-96%, and that use of the

282 intain effective weed control while reducing freshwater toxicity.

283 s and biogeochemical processes that occur in freshwater under anthropogenic eutrophication could lead

284 TMFs were more variable in marine than freshwaters, unrelated to latitude, and highest in food

285 k for transgressing regional constraints for freshwater use as a result of overconsumption of blue wa

286 Taxonomic analysis suggests that these freshwater virophages represent at least three new candi

287 tween populations under contrasting abiotic (freshwater vs. saltwater) and biotic stresses (low rates

288 For comparison, surface freshwater was collected, and LSA were generated in the

289 Plankton are vital components of marine and freshwater water-column ecosystems.

290 Here, five freshwater wetland mesocosms were exposed to 3 g of tota

291 Everglades stimulate sulfidic conditions in freshwater wetland sediments that affect ecological and

292 gical range for key archaeal taxa in a model freshwater wetland, and links these taxa and individual

293 ane production in well-oxygenated soils of a freshwater wetland.

294 oils sampled across a model methane-emitting freshwater wetland.

295 r their sulfidized forms are introduced into freshwater wetlands through wastewater effluent and agri

296 In freshwater wetlands, organic flocs are often found enric

297 n West Africa, with females mostly occupying freshwater wetlands.

298 refuge of an isolated forest patch and near freshwater with diverse edible resources.

299 Freshwater with higher blue-green algae content produced

300 yester fibers and polyethylene (PE) beads on freshwater zooplankton Ceriodaphnia dubia.