ライフサイエンスコーパス: drought

1 to differential acclimating behaviors under drought.

2 s may have modified Delta(13) C responses to drought.

3 etition caused rank changes in fitness under drought.

4 pportunities to improve our understanding of drought.

5 redictions of delayed-mortality responses to drought.

6 ble of enhancing rice growth during moderate drought.

7 n about plant performance and survival under drought.

8 -regulated poplar root growth in response to drought.

9 and microbes during, and particularly after, drought.

10 chitecture of gene expression in response to drought.

11 presence in areas that experienced postfire drought.

12 ima were separated by a period of foresummer drought.

13 ich plants were subjected to three cycles of drought.

14 all vascular plants, have few adaptations to drought.

15 g landscape irrigation, during the 2012-2016 drought.

16 ferent forms of stress, especially shade and drought.

17 >30 m) groundwater performed best during the drought.

18 al stresses such as extreme temperatures and drought.

19 n at eight out of the 10 forest sites during drought.

20 ) ) are critical to a species' adaptation to drought.

21 States, when controlling for temperature and drought.

22 ential to increase crop resilience to future drought.

23 instrumental record including the Dust Bowl drought.

24 ce of root exudates in ecosystem response to drought.

25 p = 0.001) compared with those not living in drought.

26 trophic mismatch with the green wave during drought.

27 gnificant tree mortality than the Millennium drought.

28 ee size and traits shape growth responses to droughts.

29 and intense heat waves, storms, floods, and droughts.

30 o experience hydraulic failure during severe droughts.

31 f global warming and increasing frequency of droughts.

32 nomic risks of cooling water shortage during droughts.

33 roughts in the historical record (Millennium Drought, 2000-2009 and Big Dry, 2017-2019).

34 Serbia in maize growing seasons with extreme drought (2012), extreme precipitation and flood (2014) a

35 pitation (+73.1%) but inhibited by increased drought (-30.4%), N deposition (-31.0%), and combination

36 ect of microplastics (i.e., microfibers) and drought, a factor with which microfibers might interact,

37 CE investigations of the value of traits for drought adaptation to be conducted under more severe dro

38 insights into plant habitat distribution and drought adaptation.

39 o Amazonian tropical forests and can, during drought, affect larger areas than deforestation itself.

40 and vegetation dynamics, and focuses on how drought affects interactions between conifer trees and b

41 eficial soil microbial communities, and that drought affects the quantity and quality of root exudati

42 the reservoir fills; and a severe multi-year drought after the filling.

43 migratory route, mule deer closely followed drought-altered green waves during migration.

44 tic sample, 10.7% (9,019) experienced severe drought and 23.4% (19,639) experienced mild/moderate dro

45 ese differences in vulnerability to climatic drought and climate change.

46 We imposed drought and competition treatments on diverse genotypes.

47 d-use change act synergistically, increasing drought and fire frequencies, converting several tropica

48 s in external morphology and wood anatomy to drought and fire were similar to those of some modern tr

49 years, we evaluated the effects of a natural drought and in situ experimental warming on density-depe

50 ttle is known about the relationship between drought and intimate partner violence (IPV).

51 red hypothesized mediating variables linking drought and IPV, prohibiting a formal mediation analysis

52 ing the statistics, physics, and dynamics of drought and its causes in a historical context.

53 Estimates were up to 21% and 4% higher when drought and O(3) stress were neglected respectively.

54 With the inclusion of drought and O(3) stress, GPP at CPZ, BLO and HYY is proj

55 for expanding water security in the face of drought and other water hazards.

56 With a 19 year dataset on drought and plant phenology across 99 unique migratory r

57 neous selection has higher correlations with drought and plant productivity under warming than contro

58 Under prolonged drought and reduced photosynthesis, plants consume store

59 oupled with fine root growth dynamics during drought and return of soil moisture.

60 Hyperosmotic stress caused by drought and salinity is a significant environmental thre

61 Abiotic stresses, including drought and salinity, trigger a complex osmotic-stress a

62 at occurred in California following a 4-year drought and widespread pest outbreaks.

63 utheast Asian region following unprecedented drought and wildfires.

64 tion, these events have been linked to flash droughts and can play a critical role in the spread of h

65 ican (SA) societies are highly vulnerable to droughts and pluvials, but lack of long-term climate obs

66 gest SA will experience more frequent/severe droughts and rainfall events as a consequence of increas

67 eb dynamics in coastal and shelf areas where droughts and stratification lead to increasing nutrient

68 Here we show that increasingly severe droughts and temperature driven reductions in growing se

69 ntially expressed during pathogen infection, drought, and abscisic acid treatment.

70 understanding of g(s) dynamics over seasonal drought, and identifies a practical, trait-based approac

71 ationship between rain, extreme rain, flood, drought, and season (rainy vs. dry) and diarrheal illnes

72 ich species and trees are most vulnerable to drought, and the underlying mechanisms have remained elu

73 CEs potentially causing high-impact floods, droughts, and fires.

74 is-element in intronic poly(A) sites used in drought- and heat-stressed plants that might play an imp

75 ategies affected species responses to severe drought; and how potential rooting depths varied across

76 a's 2019-2020 mega-fires were exacerbated by drought, anthropogenic climate change and existing land-

77 Robust shifts in seasonal drought are most apparent during the cool season; when s

78 scale assessments of vegetation responses to drought are needed to anticipate, manage, and potentiall

79 nges in precipitation, changes in ecological drought are robust over large portions of drylands in th

80 Extensive droughts are consistent with the observed 20th-century t

81 which are becoming as severe and frequent as droughts, are overlooked and their impacts remain poorly

82 With California's 2013-2016 extraordinary drought as a natural experiment, we studied four co-occu

83 f permeability in maize seedlings exposed to drought as well as abscisic acid treatment, which implie

84 ochemical processes; however, no global snow drought assessments currently exist.

85 PRLT2/89-33 has an inherent ability to sense drought at both developmental stages.

86 nces our understanding of plant responses to drought at regional scales.

87 scPDSI) dataset to derive the South American Drought Atlas (SADA) over the continent south of 12 degr

88 sponse to drought events: those dominated by drought-avoiding species showed strong covariance betwee

89 precipitation and increased temperature and drought, bar-built estuaries have transitioned from loti

90 We find that snow droughts became more prevalent, intensified, and lengthe

91 nt stresses, such as nutrient deficiency and drought, before the onset of visible symptoms and subseq

92 -driven risks to forest stability from fire, drought, biotic agents, and other disturbances.

93 We found no evidence of drought-buffered routes.

94 ears transition into ecological traps during drought but also highlight that some pools serve as refu

95 ty level, shoot and root mass decreased with drought but increased with microfibers, an effect likely

96 is related to the ability to survive future droughts by using a tree-ring database of surviving and

97 our experiment suggests that even short-term droughts can have extended consequences for stream ecosy

98 ikely contribute to observed changes in snow drought characteristics.

99 Extreme climate events such as droughts, cold snaps, and hurricanes can be powerful age

100 We observed genotype-drought-competition interactions for relative fitness: c

101 precipitation and flood (2014) and moderate drought conditions (2013 and 2015).

102 The latter seems to be essential under drought conditions and explains the intense occurrence o

103 adaptation to be conducted under more severe drought conditions and variable timing of drought stress

104 nts of 1983, 1997/98 and 2015/16, indicating drought conditions with less river runoff, rainfall and

105 lone criterium for quantifying and reporting drought conditions.

106 me pools serve as refuges even under extreme drought conditions.

107 that described in modern trees experiencing drought conditions.

108 s, ranging from frequent downpours to severe droughts, could cause widespread, but largely unknown, a

109 In neither drought did CABLE predict that trees would have reached

110 ether embolism formation in the xylem during drought drives this leaf mortality.

111 rsal also altered soil community response to drought; drought had a stronger effect on bacterial (but

112 olling the gene expression constitutively or drought-dynamically are unraveled.

113 has increasingly influenced the severity of drought events by decreasing runoff efficiency in the ba

114 exico, provide unambiguous evidence for five drought events that impacted the Ancestral Puebloan soci

115 data has been widely used for characterizing drought events.

116 e carbon carrying capacity adjusts to severe drought events.

117 Forest types varied in response to drought events: those dominated by drought-avoiding spec

118 moisture recycling and resulted in increased drought extent and severity, and subsequent fire.

119 en weeks, resulting in disruptive heatwaves, droughts, flooding, snowfalls, and cold spells.

120 igher basin-wide precipitation and increased drought frequency and severity.

121 concentrations, coupled with an increase in drought frequency due to climate change, pose a threat t

122 unities are discussed for new innovations in drought gene discovery using platforms targeting the ext

123 reduced recovery (low capacity to attain pre-drought growth rates) in gymnosperms.

124 altered soil community response to drought; drought had a stronger effect on bacterial (but not fung

125 Women living in mild/moderate drought had higher risk of reporting physical (marginal

126 ritical trait for predicting survival during drought, had highly species-specific responses: in one s

127 The loss of stable coexistence when drought has different effects on the competing aphid phe

128 we show that tree mortality concomitant with drought has led to short-term (mean 5 y, range 1 to 23 y

129 Drought has many known deleterious impacts on human heal

130 Drought has promoted large-scale, insect-induced tree mo

131 d mortality and community dynamics following drought have major ecological and societal impacts.

132 tural and demographic impacts of a series of droughts have primarily been developed from the environm

133 isturbance, largely during periods of severe drought, have affected as much of the forest area in the

134 occurrence of APA in Sorghum in response to drought, heat, and salt stress.

135 Each year, abiotic stress conditions such as drought, heat, salinity, cold and particularly their dif

136 the responses of 20-53 species to an extreme drought in a seasonally dry tropical forest in Costa Ric

137 a (SSA) resulted in the Cape Town "Day Zero" drought in early 2018.

138 As climate change drives increased drought in many forested regions, mechanistic understand

139 belowground microbial community response to drought in temperate maize agroecosystems, as well as ho

140 The evidence indicates a prolonged drought in the likely western source region for these co

141 period included the recent, severe regional drought in the western United States (2012-2016).

142 and 23.4% (19,639) experienced mild/moderate drought in the year prior to the survey, with substantia

143 ere is a consensus about negative impacts of droughts in Amazonia.

144 recently been subjected to two of the worst droughts in the historical record (Millennium Drought, 2

145 We assessed how growth resilience to severe droughts, including its components resistance and recove

146 [CO(2) ], increased precipitation, increased drought, increased N deposition, and their combinations)

147 Climatic factors, such as the drought index and growing degree days (GDD), had a signi

148 climate, chiefly median Palmer Hydrological Drought Index and other aridity metrics.

149 SDI exhibits consistency with meteorological drought indices in both basins.

150 ivity measurements (Lp(r) ), we examined how drought-induced changes in anatomy and hydraulic propert

151 The drought-induced decrease in NEP, which mostly occurred i

152 any ATPases) completely halted recovery from drought-induced embolism for up to 24 h after re-irrigat

153 now little about its ability to recover from drought-induced embolism.

154 make regional-scale predictions of potential drought-induced hydraulic failure.

155 there is a large variation in the degree of drought-induced leaf death across the canopy, to test wh

156 ease under anthropogenic climate change, and drought-induced mortality and community dynamics followi

157 determining the physiological mechanisms of drought-induced mortality in woody plants and identifyin

158 vel models that simulate the carbon costs of drought-induced plant hydraulic failure are improving pr

159 arming had few direct effects, but amplified drought-induced reductions in whole-tree g(m) .

160 the petiole strongly correlated with area of drought-induced tissue death in individual leaves.

161 As a physical response to water loss during drought, inner Selaginella lepidophylla stems curl into

162 with fluvial entrenchment during periods of drought, instead of being related to destructive invasio

163 As climate change-induced droughts intensify, tall trees with drought-sensitive le

164 Drought is a critical stressor that contributes to water

165 o too do the effects of environment, as when drought is amplified by competition.

166 Forest vulnerability to drought is expected to increase under anthropogenic clim

167 The capacity of trees to withstand drought is likely to be determined by traits associated

168 ence is rising that its resilience to severe drought is limited.

169 Drought is one of the main constraints in peanut product

170 rn United States during periods of prolonged droughts is poorly understood as regional hydroclimate r

171 unities experience more frequent and extreme droughts, it is increasingly important that water suppli

172 xperienced decreases in occurrence following drought-like conditions, while widespread species were u

173 of identifying robust changes in ecological drought may be useful for other assessments of climate i

174 Drought mortality increased dead tree and surface fuel c

175 Additionally, we analyzed the effects of drought- mortality on second-entry burn emissions and co

176 s the Upper Missouri River Basin, the recent drought of 2000 to 2010, known as the "turn-of-the-centu

177 We investigated the responses to drought of key fitness-related traits such as stomatal r

178 Droughts of the future are likely to be more frequent, s

179 m experiment, we investigated how impacts of drought on boreal stream ecosystems are altered by the s

180 tance may have underestimated the impacts of drought on gymnosperm-dominated forests under future cli

181 successional forests have been resilient to drought over the past 18 years, from the perspective of

182 studies have combined FACE with temperature, drought, ozone, and nitrogen treatments.

183 draulic conductivity and dye staining during drought progression and short-term (2 d) and long-term (

184 , they have not been as widely used in other drought-prone regions throughout the rest of the world,

185 species-specific mortality rates during the drought ranged from 0% to 34%, and varied little as a fu

186 Drought reduced whole-tree g(m) .

187 In angiosperms, drought-related mortality risk is associated with lower

188 Drought-related tree mortality is now a widespread pheno

189 cent reduction in vegetation greenness under droughts relative to baseline moisture conditions.

190 s were less resilient to previous non-lethal droughts, relative to coexisting surviving trees of the

191 Following drought release, we found a gradual recovery of leaf gas

192 an adjust hydraulic traits when experiencing drought remain rare.

193 ter deficits (e.g., mild, moderate or severe drought) remain elusive.

194 nagers, early career scientists, and veteran drought researchers will likely see opportunities to imp

195 neer improved water-use efficiency (WUE) and drought resilience in C(3) plants while sustaining produ

196 In particular, drought resilience markedly increased, but resistance de

197 osperms showed different spatial patterns of drought resistance and resilience, driven by variations

198 nt nf-yb21 exhibited reduced root growth and drought resistance.

199 , which ultimately increased root growth and drought resistance.

200 nd provides insights relevant to breeding of drought-resistant crops.

201 From a drought-resistant cultivar of Oryza sativa (rice), we is

202 Additionally, differential drought response among retained paralogous pairs suggest

203 oles of CDK8 in modulating ABA signaling and drought responses.

204 the coevolution of the EDS1/PAD4 pathway and drought responses.

205 N is required for HSFA6a to regulate ABA and drought responses.

206 ing early generation selection for selecting drought-responsive genotypes.

207 While 12% of the drought-responsive transcripts have similar dynamics in

208 itannins with antimicrobial properties under drought reveals an adaptive response by fine roots to pr

209 two lavender species exposed to a series of drought/rewatering cycles that varied in drought-stress

210 g than they have been in recent decades, but drought risks will be lower if greenhouse gas emissions

211 ption of various abiotic stresses, including drought, salinity, flooding, and temperature stress.

212 um experimental system that compares between drought-sensitive (ICSB338) and enhanced drought-toleran

213 -induced droughts intensify, tall trees with drought-sensitive leaves will be most vulnerable to imme

214 ant variety, but recovery is impaired in the drought-sensitive sorghum variety.

215 We quantified the drought sensitivity of vegetation in the Pacific Northwe

216 However, variability in drought sensitivity was considerable within biomes and w

217 We found that in addition to climatic drought severity (i.e., rainfall), subsurface processes

218 e this network with a self-calibrated Palmer Drought Severity Index (scPDSI) dataset to derive the So

219 stream habitats, a consequence of increasing drought severity.

220 ungulates to surf, little is known about how drought shapes the green wave and influences the foragin

221 western Wyoming, United States, we show that drought shortened the duration of spring green-up by app

222 mmediate transcriptional response to ABA and drought signals.

223 Differential miRNA expression among drought specific tissues indicted the probable energy co

224 ach of 15 years, data were based on reported drought status for August, wetland cover, the physiograp

225 SCA at MLO is mainly exerted by intensified drought stress acting to offset the acceleration driven

226 elevated temperatures, CO(2) concentrations, drought stress and nutrient conditions directly and indi

227 ips1 (nut1), that mimics tassel blasting and drought stress and reveals the genetic mechanisms underl

228 of comparative transcriptome analysis under drought stress at two different developmental stages whi

229 l the study sites was obtained with O(3) and drought stress combined, such that the two stressors cou

230 ere was some evidence that the timing of the drought stress during crop growth influenced the effect

231 s, using our existing data on the effects of drought stress in crops as an example.

232 nnual plants, higher temperatures, CO(2) and drought stress increase foliar herbivory.

233 ly, we find no signal for stochasticity when drought stress is relieved, likely due to renewed select

234 When exposed to drought stress many plants reprogram their gene expressi

235 We found drought stress was the more significant as it reduced mo

236 re drought conditions and variable timing of drought stress, a risky but necessary endeavour.

237 ghum was shaped by diversifying selection on drought stress, and can inform genomics-enabled breeding

238 ent physiological changes to mild and severe drought stress, and the associated transcriptome dynamic

239 ays an important role in plant adaptation to drought stress, but the underlying molecular mechanisms

240 further reflects pressures to avoid frost or drought stress.

241 d stomatal apertures and hypersensitivity to drought stress.

242 how forest carbon fluxes respond to heat and drought stress.

243 in rice roots and is strongly responsive to drought stress.

244 tolerant genotype, PRLT2/89-33, subjected to drought stress.

245 a C(4) herb capable of performing CAM under drought stress.

246 of drought/rewatering cycles that varied in drought-stress intensity.

247 arly in host development and when sorghum is drought stressed, conditions when mycobiomes are small.

248 almeriense mycorrhiza from well-watered and drought-stressed plants, when intracellular colonization

249 This failure to adjust resulted in these drought-stressed trees experiencing significantly lower

250 traits relating to plant hydraulic stress in drought-stressed trees.

251 mers had traits conferring more tolerance to drought such as small sclerophyllous leaves and lower pe

252 n woody plants and identifying thresholds of drought survivorship will improve forecasts of forest an

253 ent, lower reproductive potential and higher drought susceptibility.

254 ental stage in fine roots of 101-14Mgt (i.e. drought susceptible), probably limiting cortical lacunae

255 thin protected forests was more resilient to drought than within non-protected forests.

256 mber of foliar functional traits affected by drought that can be used as indicators of plant water st

257 Our study revealed that, when exposed to drought, the composition of heteropolymers are strategic

258 Cassava is cultivated due to its drought tolerance and high carbohydrate-containing stora

259 Clusters associated with improved drought tolerance consisted of phene states that likely

260 ction and leading to greater WUE(i) provides drought tolerance in Caragana species adapted to low-MAP

261 stic understanding of the factors conferring drought tolerance in trees is increasingly important.

262 At present, the molecular basis of terminal drought tolerance of certain pearl millet genotypes rema

263 Two proteins involved in drought tolerance were also identified.

264 y and environmentally relevant traits (e.g., drought tolerance); however, incorporating high-dimensio

265 d, while knockdown of ZmPTPN inhibited plant drought tolerance, indicating conserved and positive rol

266 her morpho-physiological traits related with drought tolerance.

267 is verified to play a negative role in plant drought tolerance.

268 growth rates as expected by a trade-off with drought tolerance.

269 onserved and positive roles of PTPN in plant drought tolerance.

270 which can facilitate fastidious discovery of drought tolerant genes leading to improved yield in pear

271 egetative and flowering stages of a terminal drought tolerant genotype, PRLT2/89-33, subjected to dro

272 een drought-sensitive (ICSB338) and enhanced drought-tolerant (SA1441) varieties.

273 STS dimension reflected segregation between drought-tolerant and waterlogging-tolerant species.

274 Moench.), a drought-tolerant C4 grass, contain up to 50 nodes and in

275 greenness and SPEI, while those dominated by drought-tolerant species showed weak covariance.

276 Surprisingly, neither immigrants nor drought-tolerant taxa had higher abundance in dispersal

277 rdinated shifts toward communities with more drought-tolerant traits driven by tree mortality, but th

278 mitation (within 24 h of re-watering) in the drought-tolerant variety, but recovery is impaired in th

279 g treatments, a well-watered treatment and a drought treatment in which plants were subjected to thre

280 However, the physiological linkages among drought, tree defences, and insect outbreaks are still u

281 a juniper (Juniperus californica), examining drought vulnerability as a function of climate, litholog

282 subsurface processes explained variation in drought vulnerability within and across species at both

283 and other environmental stressors, including drought, warming and nutrient stress.

284 Our findings indicate that drought was associated with measures of IPV towards wome

285 sture to demonstrate that the 2000-2018 SWNA drought was the second driest 19-year period since 800 C

286 0 to 2010, known as the "turn-of-the-century drought," was likely more severe than any in the instrum

287 most extensive database available on shade, drought, waterlogging and cold tolerance for 799 norther

288 warming-amplified beetle life cycles whereas drought-weakened host defenses appear to have been a dis

289 r plants are not able to recover from severe drought when they have used up their elastic water stora

290 low capacity to reduce impact of the initial drought), while it is related to reduced recovery (low c

291 creased in the distal root orders exposed to drought, while the fiber-bound condensed tannnins increa

292 cultivation were initiated during periods of drought, with periods of forest recovery occurring durin

293 sult from additional reported occurrences of drought, with reported losses due to heat stress playing

294 Our results suggest that drought, without mandatory water use restrictions, may c

295 uch as 23-33% below the field average during drought years and 26-33% during deluge years.

296 f pools with reduced or zero survival during drought years and a coincident increase in spatial varia

297 er growing, more stress-resistant species in drought years and/or chronically drier climate.

298 y of predicting the location of catastrophic drought years in advance.

299 at many pools sustain juvenile salmon in non-drought years transition into ecological traps during dr

300 olism is a major cause of plant death during drought, yet the spread of embolism throughout the plant