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1 pes as a function of geology, topography and climate.
2 ole it can play in stabilizing future global climate.
3 ding of the ocean's influence on weather and climate.
4 ects of soil structure on surface fluxes and climate.
5 ormation rather than a direct consequence of climate.
6 -native populations-under a rapidly changing climate.
7 of tree longevity and growth rates to future climate.
8 (N(2)O) plays a critical role in the global climate.
9 times commensurate with the pace of changing climate.
10 sity conservation in the context of changing climate.
11 egional and global atmospheric chemistry and climate.
12 the effects of ageing forests from variable climate.
13 dynamics are highly sensitive to changes in climate.
14 ility of species range edges with a changing climate.
15 ven in large part by changes to land use and climate.
16 ence of these migrations, or with changes in climate.
17 ivity and resistance to pathogens in adverse climates.
18 onditions simulating shipping in hot or cold climates.
19 ent scenarios for field sites across various climates.
20 ciation rates ~2-fold below rosids in cooler climates.
21 ologies to further insights gained from past climates.
22 t generally remains unclear which changes in climate actually cause extinctions, and how many species
23 e and fluvial connectivity will be important climate adaptation tactics for conserving aquatic biodiv
24 We then applied this method to calculate climate-adjusted water quality guideline values (GVs) fo
26 ons in large areas of the globe, influencing climate, air quality, and human health in open seas and
30 eography ultimately arises from gradients of climate and biogeochemistry with implications for the ge
32 anges in climatic and atmospheric processes, climate and ecological dipoles are likely to shift in th
34 mplications of a positive feedback to global climate and emphasize the close linkage between soil mic
39 ritical for predicting the effects of future climate and land-use change on plants, pollinators, and
40 op between Amazonian BVOCs and the trends of climate and land-use changes in Amazonia is then constru
46 fundamental role in global water resources, climate, and biogeochemical processes; however, no globa
47 tify the top influential factors among soil, climate, and farming practices, which drive the spatial
48 polygenic adaptation of SHB to the southern climate, and may be relevant for future population-scale
51 ered across the range of recent interglacial climate backgrounds, which demonstrates that catastrophi
52 rly successional >= restored prairie; direct climate benefits ranged from ~80% (stover) to 290% (rest
53 Forests are critical for stabilizing our climate, but costs of mitigation over space, time, and s
54 nge in plant functional traits under warming climate, but studies on one key factor, snow cover, are
58 tperformed local populations under simulated climate change (snow removal) across all five experiment
59 revealed that 82% of real-world examples of climate change adaptation in MPA planning derive from tr
61 tal hazards as declining sediment supply and climate change alter their sediment budget, affecting de
62 ility is fundamental to predicting near-term climate change and changing extremes, and to attributing
64 es due to latitudinal range shifts driven by climate change and increased artificial light at night (
67 rts to predict how consumers will respond to climate change and other environmental perturbations.
68 f sudden and severe biodiversity losses from climate change and provide a framework for predicting bo
69 able potential to help mitigate human-caused climate change and provide society with many cobenefits.
70 e promise of mitigating the worst effects of climate change and providing a means to engineer crops f
71 maladaptive in the context of anthropogenic climate change and that selection now promotes thermal c
73 Rising atmospheric CO(2) is intensifying climate change but it is also driving global and particu
74 gle field of research that could help combat climate change by generating better heat pumps for both
79 rbate the impacts of biological invasions if climate change differentially affects invasive and nativ
81 udies have not addressed the consequences of climate change for the metabolism of these organisms in
90 on data also suggest an accelerating role of climate change in the range expansion of M. soledadinus,
91 dicting how organisms will respond to future climate change is a challenging task for biologists.
99 uced species are one mechanism through which climate change may exacerbate negative impacts of biolog
100 rstanding how species have responded to past climate change may help refine projections of how specie
103 of the potential contributions of forests in climate change mitigation associated with tree planting.
105 ered to determine whether planting trees for climate change mitigation results in increased C storage
107 n (the Master Plan) on population health and climate change mitigation, assuming primary, sustained u
108 been proposed as a means to sequester C for climate change mitigation, yet little is known about how
110 tudies have estimated the adverse effects of climate change on crop yields, however, this literature
113 ive, whereas the likely outcome of continued climate change on summer survival was generally positive
114 s expanding into new habitats as a result of climate change or human introductions will frequently en
118 ted CO(2) and warmer temperatures reflecting climate change scenarios somewhat attenuated nanoplastic
121 become aware that responses of holobionts to climate change stressors may be driven by shifts in the
122 indirect effects, we used the simulations of climate change to assess the distribution of P. smintheu
126 capacity all contribute to heterogeneity in climate change vulnerability, predicting these features
127 preceding summer and the effect of continued climate change was likely to be mainly negative, whereas
129 unlikely.(1-3) Eutrophication, overfishing, climate change, and disease have fueled the supremacy of
131 ions (NO) lead to increased smog, acid rain, climate change, and respiratory inflammation within the
132 esponse of caribou reproductive phenology to climate change, and species-specific changes in terrestr
133 communities exhibit a range of responses to climate change, and that improving passage and fluvial c
135 he most dramatic damage due to anthropogenic climate change, and the situation is predicted to worsen
137 resented in studies demonstrating effects of climate change, but depending on their thermal tolerance
138 nge are governed by ecosystem sensitivity to climate change, but ecosystem model projections are unde
139 and biomes to shift poleward and upward with climate change, but non-climatic factors complicate thes
140 l conditions could increase vulnerability to climate change, even for geographically widespread speci
141 If these processes continue during modern climate change, future loss of summer Arctic sea ice wil
143 tical role of coastal wetlands in mitigating climate change, sea-level rise, and salinity increase, s
144 Fast ecological responses closely track climate change, slow responses substantively lag climate
147 While MREDs undoubtedly can help mitigate climate change, variability in the sensitivity of differ
148 ten discussed as "co-benefits" of mitigating climate change, yet they are rarely considered when desi
149 , we assess the likely effects of four major climate change-related abiotic factors on the spatiotemp
150 dy permits spatially explicit predictions of climate change-related population extinction-colonizatio
177 tinction due to human land use, hunting, and climate change; (ii) loss of megabiota has a negative im
189 limate varies due to human activity, natural climate cycles, and natural events external to the clima
190 f area index data from satellites along with climate data estimated localized phenological parameters
194 during litter decomposition will change with climate, driven primarily by indirect climate effects (e
197 ggest that evolution at Eda is a response to climate-driven habitat transformation rather than a dire
198 sent exposure to natural hazards, and future climate-driven shifts in their distribution, frequency,
200 Improved knowledge of species' responses to climate dynamics will allow us to anticipate and manage
202 e with climate, driven primarily by indirect climate effects (e.g., greater nitrogen availability and
203 e simulations producing temporal dynamics of climate en route to stable global mean temperature at 1.
205 ors of green seaweeds survived these extreme climate events in isolated refugia, and diversified in b
208 sions respond to interannual and longer-term climate fluctuations and close to half the world's lake
209 ture, sustainable food systems, reduction in climate forcing agents, and reduction in wildfires.
211 ate change, slow responses substantively lag climate forcing, causing disequilibria and reduced fitne
215 e the spatial structure of range edges along climate gradients, and we discuss several ways that thes
219 gy to simultaneously alleviate CO(2) -caused climate hazards and ever-increasing energy demands, as i
220 ul tool with reasonable skill to provide the climate-health outlook about possible disease incidence
221 pirical support, we argue that three factors-climate heterogeneity, collinearity among climate variab
222 lowing forest establishment, but the role of climate in driving these trends has not been explored.
224 to the vulnerability of forest landscapes to climate-induced productivity losses and mortality events
225 ally due to geographic genetic variation and climate interactions with other aspects of environment.
228 redicting how tropical deforestation affects climate is the lack of baseline conditions (i.e., prior
230 ining drought vulnerability as a function of climate, lithology and hydrology using regional aerial d
232 level of understanding, we conclude that the climate mitigation induced by increased SOC storage is g
234 under eCO(2), and challenge the efficacy of climate mitigation strategies that rely on ubiquitous CO
236 mes and apply the resulting relationships to climate model data in a risk-based attribution methodolo
237 sea level pressure data from a large set of climate model simulations and, as a proxy for observatio
242 itation projections vary substantially among climate models, enhancing variation in overall trajector
244 ver an annual grassland in the Mediterranean climate of California, USA, from 2001 through 2019 with
245 ned if genotypic variation is related to the climate of genotype provenance and whether phenotypic pl
246 lexity and sub-tropical to temperate growing climate of Louisiana warrant a region-specific core coll
247 framework to assess the impacts of changing climate on water resources for the Alabama-Coosa-Tallapo
249 flow across species, mediated by Quaternary climate oscillations that have facilitated a dynamic of
250 no-Southern Oscillation (ENSO) shapes global climate patterns yet its sensitivity to external climate
251 ey been used to investigate the influence of climate perturbation on potentially dangerous natural ph
254 he relevancy of paleoclimate information for climate prediction and discuss the prospects for emergin
255 n Modeling System (ROMS) to downscale global climate predictions across all Representative Concentrat
257 hropocene and other eras of rapidly changing climates, rates of change of ecological systems can be d
259 ersity and multifunctionality, how different climate regimes alter the stability and functions of the
261 ese Mediterranean-like regions, future hydro-climate-related impacts will be substantially modulated
264 r estimate that, under a 'business-as-usual' climate scenario, earlier spring arrival will enhance NP
267 t variable for adequately characterizing the climate sensitivity of cooling load, and that near-surfa
268 O(2) Oligocene world (~300 to 700 ppm), warm climates similar to those of the late Eocene continued w
271 orld endanger the functioning of ecosystems, climate stability, and conservation of biodiversity.
272 The dramatic reorganization of the Asian climate system coincident with Oi-1 was, thus, a respons
273 tions appears to reflect the response of the climate system to both anthropogenic and natural forcing
276 ential to drive more ambitious action toward climate targets than governments, thus driving the neces
277 on of oceans and the atmosphere and thus the climate, the microbial world is bound to change and adap
278 counting approach, GHG metric, time horizon, climate threshold, global emissions budget calculation m
279 romotion and delay of flowering in different climates to balance survival and, through a post-vernali
280 ies, we show that when dispersal ability and climate tolerance are restricted, microclimatic variatio
281 y diverse western US, using data on observed climate trends from 1948 to 2014 to highlight emerging p
282 , statistical associations with 20th century climate trends, and whether advance rates match climate
283 case count data, to investigate the role of climate, urbanization and variation in interventions.
285 mospheric mode that controls winter European climate variability because its strength and phase deter
286 n agreement with multidecadal North Atlantic climate variability derived from independent proxies.
287 rs-climate heterogeneity, collinearity among climate variables, and spatial scale-interact to shape t
290 will likely take far longer (centuries) than climate warming (decades), so in the short-term, tree re
293 Resilience to environmental stressors due to climate warming is influenced by local adaptations, incl
298 osition of this vast C bank could accelerate climate warming; however, the likelihood of this outcome
299 bitats proved more susceptible to changes in climate, with hotter and drier periods associated with g
300 s were consistent across ecosystem types and climate zones, with local characteristics explaining muc