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1 y facilitating compensatory growth following drought.
2 riety of environmental conditions, including drought.
3 d were retained across periods of heightened drought.
4 ther the decline and mortality are driven by drought.
5 urvival capabilities of plant species during drought.
6 ) has been nearly reached during the current drought.
7 at causes ecosystems to shift in response to drought.
8 of future TWS impacts including flooding and drought.
9 y a particular role in shoots in response to drought.
10 an help cope with the detrimental effects of drought.
11 ising dramatically during the fourth year of drought.
12 change and CO2-induced warming) to the 2016 drought.
13 ecame prevalent as a response to the extreme drought.
14 ers were also measured before and during the drought.
15 ion to male organs (stamens) decreased under drought.
16 anism for plants and ecosystems to cope with drought.
17 ient in Panama that have experienced El Nino droughts.
18 treatments further modified the severity of droughts.
19 aits under increased temperature and intense droughts.
20 under mild to moderate soil and atmospheric droughts.
21 severe and extensive than the 2005 and 2010 droughts.
26 but an increasing frequency and intensity of drought across northern ecosystems is threatening to dis
29 ize how C cycling is shaped by tree size and drought adaptations and how these patterns relate to spa
32 e analyse and model the impact of coincident drought and antecedent wet conditions (proxy for the cli
33 terest of breeders for its high tolerance to drought and as potential genetic source in breeding prog
35 r, many turfgrass species are susceptible to drought and demand frequent irrigation thus consuming la
36 accumulation trends of miRNAs, observed upon drought and in different genotypes and organs, were conf
37 a and attempted to investigate the effect of drought and insect outbreaks on growth decline, and simu
39 , most studies only provide singular view of drought and lack the integration with specific crop phen
40 of ecosystem C to 8-12 years of experimental drought and night-time warming across an aridity gradien
41 indicate the conserved role of this gene in drought and other abiotic stress tolerance in several pl
43 h this crop displays high productivity under drought and poor soil conditions, it is susceptible to d
45 e vulnerability of electric power systems to drought and the potential for both climate change and a
46 ntial and foliar abscisic acid (ABA), during drought and through the subsequent rehydration period fo
47 rstanding of the biological responses during droughts and contributes to elucidate the molecular mech
48 results show that frequency and severity of droughts and floods can have characteristic effects on t
50 Brachypodium dystachion to single salinity, drought, and heat stresses, as well as their double and
51 ccumulated upon high temperatures, UV-light, drought, and nutrient deficiencies, and may contribute t
52 y from reduction in vegetation uptake due to drought, and to a lesser degree from increased biomass b
54 e ecohydrological consequences from the 2016 drought are more severe and extensive than the 2005 and
56 evidence, the interactions between fires and droughts are a more direct mechanism that may describe s
61 gion vulnerable economically and socially to drought, but glaciers are a uniquely drought-resilient s
62 increased xylem sap sulfate is achieved upon drought by reduced xylem unloading by PtaSULTR3;3a and P
65 ter table; in between, high productivity and drought can send roots many meters down to the groundwat
70 upport previous findings from peatlands that drought causes reduced magnitude of growing season FCH4
71 hubs transcription factors regulated during drought conditions in sunflower, useful for applications
74 coli were also comparable during wet versus drought conditions, and the relative abundance of strain
81 ty rates and biomass declines in response to drought depend on stomatal and xylem flow regulation.
84 n crop yield anomalies and all four kinds of drought during the wheat growing season was established.
89 longer, and more frequent global change-type drought events may profoundly impact terrestrial ecosyst
91 upon results from two large-scale ecosystem drought experiments in the eastern Brazilian Amazon that
92 sensitivity of butterflies to four extremes (drought, extreme precipitation, extreme heat and extreme
95 l-scale modeling to highlight that increased drought frequency and severity pose a formidable challen
96 same mean soil moisture, but with different drought frequency caused by wet-dry cycles of varying pe
101 study demonstrates a novel approach to study drought from multiple views and integrate it with crop g
102 hydrological, soil moisture, and vegetation droughts from 1981 to 2013 were reconstructed for the fi
105 lts indicated that prolonged and large-scale droughts had a strong negative impact on trembling aspen
106 35S::ERF74 showed enhanced tolerance to drought, high light, heat and aluminum stresses, whereas
110 of Earth's climate system) and second, that drought impacts (assessed using the area of ecosystems a
114 the NAO have been associated with a shift to drought in the areas of origin for the Cimbri, Quadi, Vi
117 nt relationship between fire and same-summer droughts in most regions, while antecedent climate condi
119 nd Atlantic were the main drivers of extreme droughts in South America, but are unable to explain the
120 terrestrial carbon (C) exchange, and recent droughts in the Amazon Basin have contributed to short-t
121 rn value in the Amazon and recurrent extreme droughts in the Nordeste region, with profound eco-hydro
123 The changes of aNPP and Rs in response to drought indicated that wet systems had an overall risk o
124 red by the two most prominent meteorological drought indices: the Standardized Precipitation Index (S
127 l and temporal domains can better reveal the drought-induced green-up phenomenon, which appears less
128 ating experimental and observational data of drought-induced mortality across the Neotropics to the l
129 investigate whether the relationship between drought-induced mortality and distributions holds contin
133 limate change, yet little is known about how drought influences plant-soil feedbacks with respect to
134 as enhanced resistance to and recovery from drought, instead arise from dynamic interactions in our
136 ignificantly higher water potentials for the drought-intolerant PFT compared to the drought-tolerant
138 ught-tolerant seedlings grew 25% larger than drought-intolerant seedlings under dry conditions when e
140 in the transcriptomic response of species to drought is a significantly better indicator of natural c
143 size that this high range edge resistance to drought is driven primarily by local environmental facto
144 portance of VPDant suggests that atmospheric drought is important for predicting GPP under current an
148 the first to reveal a regional divergence in drought likelihood as measured by the two most prominent
149 of global change, and ecological effects of drought may be compounded by other drivers, such as anth
150 more frequent, as expected, the time between droughts may become shorter than drought recovery time,
153 lts illustrate the importance of appropriate drought measures and, as a global study that focuses on
155 er field conditions to inform the design of 'Drought-Net', a relatively low-cost CDE that simulates e
156 ated the response of plant and soil fungi to drought of different intensities using a water table gra
161 limited by physical protection, but also by drought or wetting-induced shifts in hydrologic connecti
163 roved understanding and forecasting of Sahel drought, paramount for successful adaptation strategies
165 protected salt marshes experiencing a severe drought, plant-eating grazers eliminated drought-stresse
166 ering plants from water stress during severe droughts, plant water storage (PWS) alters many features
169 wever, areas of high risk were also found in drought-prone regions for beech and in the southern Alps
170 ovement has progressed slowly, especially in drought-prone regions where annual crop production suffe
171 ime between droughts may become shorter than drought recovery time, leading to permanently damaged ec
172 insights into the spatiotemporal patterns of drought recovery time: first, that recovery is longest i
175 bolism, we investigated whether the observed drought-related NO changes could involve polyamine pathw
187 s taken in the study of genetic variation in drought responses, the advantages and shortcomings of ea
189 sm in which rice plants govern ABA-dependant drought responsive gene expression by controlling the st
190 ine coracana) by cDNA subtraction identified drought responsive genes that have a potential role in d
191 1 SUMO protease directly targets the ABA and drought responsive transcription factor OsbZIP23 for de-
194 reclaimed wastewater for agriculture because drought, rising temperatures, and expanding human popula
202 Identifying vulnerable ecological systems to drought stress and climate thresholds associated with ca
205 impaired stomatal closure in response to the drought stress hormone ABA and increased whole-plant wil
206 ed tolerance to osmotic stress, salinity and drought stress in addition to conferring insensitivity t
207 el is highly induced by salt and PEG-induced drought stress in both shoots and roots in both Nipponba
208 the OsNHX1 response to salt and PEG-induced drought stress in either shoots or roots was quite simil
209 criptional and metabolic pathways related to drought stress in sunflower plants, by using a system bi
212 FACTOR 3 (GBF3) were identified as candidate drought stress response genes and the role of GBF3 in dr
214 of the molecular mechanisms involved in the drought stress responses of sugarcane impairs the develo
215 hese TFs may be associated with the salt and drought stress tolerance observed for this genotype.
218 ted the malleability of the DNA methylome to drought stress within a generation and under repeated dr
219 d water transport are critical indicators of drought stress, they can be unrelated to visible metrics
220 tified 318 lncRNAs responsive to cold and/or drought stress, which were typically co-expressed concor
229 ere drought, plant-eating grazers eliminated drought-stressed vegetation that could otherwise survive
230 parate impacts of high temperature, heat and drought stresses on the current and future US rainfed ma
231 tain, however, whether tree mortality across drought-stricken landscapes will be concentrated in part
233 availability may play a detrimental role in drought survival due to preferential biomass allocation
234 mework for understanding nutrient impacts on drought survival that allows a more complete analysis of
235 nts 'Harry' (drought tolerant) and 'Wesley' (drought susceptible) were used to develop a recombinant
236 nses to abiotic and biotic stresses, such as drought, temperature, salinity, nutrient deprivation, ba
237 ved sulfate seems to be a chemical signal of drought that induces stomatal closure via QUAC1/ALMT12 a
238 verts occurred concurrently with a multiyear drought that resulted in a decrease in the lake elevatio
239 stic description of plant response to lethal drought that would improve predictive understanding of m
240 up-regulate wax accumulation in response to drought, the hormonal regulation of cuticle biosynthesis
242 ients of manipulations, ranging from extreme drought to extreme precipitation increases into future c
243 % to +60% of ambient precipitation to form a drought to wet precipitation gradient) was conducted ove
244 Our results indicated that SeCspA conferred drought tolerance and improved physiological traits in w
245 ts demonstrate the role of GBF3 in imparting drought tolerance in A. thaliana and indicate the conser
246 ion of acetic acid successfully enhanced the drought tolerance in Arabidopsis, rapeseed, maize, rice
252 tress response genes and the role of GBF3 in drought tolerance was studied in Arabidopsis thaliana.
253 of ROS eliminating processes in response to drought tolerance were mechanisms exclusive to cv. RB867
254 e three traits are important for determining drought tolerance, and are largely independent of wood d
255 significantly enhanced water use efficiency, drought tolerance, and soil water conservation propertie
270 O2 ] for integrated plant-water dynamics and drought tolerance; and (3) CO2 effects on symbiotic inte
275 r the drought-intolerant PFT compared to the drought-tolerant PFT; however, there were no significant
276 arly when provided sterile EMF inoculum, but drought-tolerant seedlings grew 25% larger than drought-
277 lines were found for gymnosperms, shade- and drought-tolerant species, and trees that died from compe
278 tsuga menziesii) have both been described as drought-tolerant species, our understanding of their gro
283 rovide the knowledge of the most influential drought type, conjunction, spatial-temporal distribution
284 ssure internally at utilities to incorporate drought vulnerability into long-term strategic planning,
285 rs and policy-makers in identifying the most drought-vulnerable forests across broad geographic areas
286 p Brassica rapa during initial perception of drought, we applied a co-expression network approach to
288 plant and microbial responses to subsequent drought were dependent on a legacy effect of the previou
290 fferences between provenances in response to drought, where provenances sustaining higher CO2 assimil
291 rained, whereas soil moisture and ecological droughts, which drive vegetation productivity and compos
292 ibit more productive agronomic traits during drought while OsOTS1 overexpressing lines are drought se
294 llocation decreased by half in pistils under drought, while stamen phosphorus was unaffected by envir
298 sing temperatures, it is likely that severer droughts with a higher frequency will occur in western C
299 reasingly prone to climate extremes, such as drought, with long-lasting effects on both plant and soi
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