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1 ity may lead to an increase in grass in this biome.
2 /GPP remains approximately constant within a biome.
3 n previous estimates for the tropical forest biome.
4 characteristic drought time-scales for each biome.
5 genetic variation across the xeric Caatinga biome.
6 Bee responses varied slightly by biome.
7 nge of temperatures that occur in the tundra biome.
8 taxonomic units identified in a given ICoMM biome.
9 insights into the assembly of this important biome.
10 of deforestation in this globally important biome.
11 ica, which represent an arid, lower-latitude biome.
12 influencing the net C balance of the tundra biome.
13 identification of multiple species within a biome.
14 vannas in what is otherwise a highly dynamic biome.
15 eneral 'greening' trend in the arctic tundra biome.
16 tive net CO2 uptake trends across the boreal biome.
17 nd least explored resource in this inspiring biome.
18 l work has been limited in scope to a single biome.
19 and response to disturbance) in the tropical biome.
20 esearch Council, AstraZeneca UK, US Army, EU-Biomed.
21 st of P acquisition varies only 2-fold among biomes.
22 lower productivity when compared with other biomes.
23 of decentralization, especially in tropical biomes.
24 ation responses across disturbance types and biomes.
25 M-associated plants in mid- and low-latitude biomes.
26 sitively with its specific leaf area in most biomes.
27 fire feedback in tropical savanna and forest biomes.
28 anging, with unknown consequences for forest biomes.
29 y information across terrestrial and aquatic biomes.
30 with implications for diversity within both biomes.
31 t biomes and 4.2 to 5.3 years for non-forest biomes.
32 ompensation in many tropical and subtropical biomes.
33 om the atlantic forest, caatinga and cerrado biomes.
34 protocol to each of the world's major forest biomes.
35 al separation is widespread across different biomes.
36 d P) additions across temperate vs. tropical biomes.
37 transforming fire regimes in many of Earth's biomes.
38 es capture major observed patterns in marine biomes.
39 genus Myrciaria occurs in various Brazilian biomes.
40 d and uninvaded plant communities from three biomes.
41 ements (R(2) > 0.7) in most of the evaluated biomes.
42 d N have shown inconsistent patterns between biomes.
43 ay invoke massive nonlinear shifts in boreal biomes.
44 d elimination among geographically separated biomes.
45 of plant and animal communities vary across biomes.
46 versity and function vary across terrestrial biomes.
47 nzymes) across a wide variety of terrestrial biomes.
48 rease moisture variability within and across biomes.
49 humid tropical, dry tropical, and temperate biomes.
50 Delta(leaf) of up to 6 per thousand between biomes.
51 d with shifts between temperate and tropical biomes.
52 rranean-type and temperate coniferous forest biomes.
53 ted areas may mitigate the problem in desert biomes.
54 rees of latitude, from subtropical to boreal biomes.
55 e effects expected to occur in high-latitude biomes.
56 y leaves of 218 plant species spanning seven biomes.
57 evolution of C4 grass- and grazer-dominated biomes.
58 obustness of such a relationship across more biomes.
59 g boreal, temperate and Mediterranean forest biomes.
60 nd for sharing of pathogens across hosts and biomes.
61 biguously extrapolate these results to other biomes.
62 irically with experiments that spanned three biomes.
63 P), and East Asia, corresponding to distinct biomes.
64 transition zone between boreal and temperate biomes.
65 -arcmin global grid, ecoregions (501 units), biomes (14 units), countries (124 units), continents, an
66 arrangements were amplified according to the BIOMED-2 protocol and PCR products were sequenced direct
67 This is across 162 sites and 12 terrestrial biomes (89% of heterogeneity explained; Q-value = 1235;
68 sion has occurred in the neighboring Cerrado biome, a biodiversity hotspot comprised of dry forests,
69 led reactive N inputs to the tropical forest biome, a far greater change than previously thought.
77 , drylands represent the largest terrestrial biome and are projected to expand by 23% by the end of t
78 it the largest fire on record for the tundra biome and doubling the cumulative area burned since 1950
79 s represent the planet's largest terrestrial biome and evidence suggests these landscapes have large
80 will be highly correlated with annual ES at biome and global scales; (2) there will be parallel patt
83 y diverse vegetation in the temperate forest biome and provide support for recent moves toward rewild
84 ch of the midwestern United States, but this biome and the soil microbial diversity that once sustain
87 mically as pollinators in cool and temperate biomes and as model organisms for scientific research.
88 importance of these factors across different biomes and at the global scale require tests of the rela
90 ift of attention to previously ignored major biomes and careful application of verified methods for v
92 evel phylogeny, and paleo-reconstructions of biomes and climate to examine Cenozoic imprints on the p
94 ble interface between terrestrial and marine biomes and even small changes in the magnitude and predi
95 ion on microbial communities across multiple biomes and explore what determines the vulnerability of
96 ge effects in the world's other major forest biomes and indicate that the strength of the temperate b
98 af forest had the highest NPP among the nine biomes and moderate residence times, leading to a relati
99 E experiments in mature forests in different biomes and over a wide range of climate space and biodiv
100 gger appear insignificantly different across biomes and plant functional types, suggesting that therm
103 -induced mortality rates differ among global biomes and whether functional traits influence the risk
105 nd biotic and abiotic factors at individual, biome, and global scales, and developed a global gridded
106 sification of the lineages that inhabit this biome, and/or a long recovery period from the terminal C
108 ine-root traits across root orders, species, biomes, and environmental gradients while also providing
109 ated negatively with its wood density in all biomes, and positively with its specific leaf area in mo
110 with drought to a maximum WUE(e) across all biomes; and a minimum native state in wetter years that
111 turnover rates of carbon pools in semi-arid biomes are an increasingly important driver of global ca
114 biome clearing occurs within only 6% of the biome area, emphasizing the presence of forest clearing
116 s likely differ from those operating in arid biomes, as plants usually have a poor adaptability to wa
118 nual net C sink for the entire Arctic tundra biome averaged over the last quarter of the twentieth ce
119 l (DGVM) that simulates the distributions of biomes based on basic plant functional types with projec
120 estimate of global forest extent in dryland biomes, based on analyzing more than 210,000 0.5-hectare
121 ugh processes and sensitivities differ among biomes, based on expert opinion, we expect forests to ex
122 y not change as intact units as predicted by biome-based modeling, but are likely to trend toward sim
123 e combine the process-based ecosystem model (Biome-BGC) with climate change-scenarios based on both R
128 rate towards higher latitudes and among some biomes, but no biogeographic patterns in the frequency o
129 have long utilized resources from all forest biomes, but the most indelible anthropogenic signature h
130 icrobial diversity that once existed in this biome by analyzing relict prairie soils and found that t
134 ncrease in fire activity, possibly caused by biome changes and accumulation of fuel related to the la
137 t loss in Brazil accounts for 47.8% of total biome clearing, nearly four times that of the next highe
139 fferential warming of tropical and temperate biomes could result in a similar proportional increase i
141 of 49 species across temperate and tropical biomes, demonstrating that the ageing rate of photosynth
142 romogenic media, which included Colorex VRE (BioMed Diagnostics, White City, OR) or Oxoid VRE (Oxoid,
143 analyse climate, CO2 and fire influences on biome distribution and net primary production (NPP) in l
144 c and natural factors contributed to current biome distribution is thus a crucial issue to understand
145 tly through photosynthesis, but also through biome distribution, which is strongly influenced by fire
151 learned from a given disturbance regime and biome (e.g. crown-fire Mediterranean ecosystems) can gui
156 oxide measurements, we derived the basin net biome exchange (that is, the carbon flux between the non
158 portance for the global carbon budget is net biome exchange of CO2 with the atmosphere (NBE), which r
161 of soil fauna on decomposition rates between biomes, from climate-driven biomes to those where climat
162 rasting ecosystem responses, differing among biomes globally, independent of changes in mean precipit
164 fication and extinction rates, and evaluated biome/habitat and geographic shifts in Detarioideae.
166 nstructed ancestral states for geography and biome/habitat, estimated diversification and extinction
167 ter availability across the temperate forest biome have the potential to offset gains in carbon (C) u
170 or eliminated the importance of latitude and biome in predicting outcrossing or self-incompatibility.
173 rders of magnitude), and habitats (all major biomes) in our database allows us to quantify novel feat
174 ed with water availability within and across biomes, indicating power for anticipating drought respon
177 iversity have mainly focused on whether this biome is an evolutionary 'cradle' or 'museum', emphasizi
183 Despite their ecological importance for many biomes, knowledge regarding herb hydraulics remains very
184 is synthesis identifies the need to consider biome, landscape position, and vascular/moss vegetation
186 do this, we create a new dataset that merges biome-level associations for all monocot genera with cou
189 Resilience of rainfed agriculture in both biomes likely depends on water recycling in undisturbed
190 hropologic as well as natural changes in the biome may have effects on IgE sensitization profiles alr
191 ents such as the Brazilian semiarid Caatinga biome may reveal how severe climate conditions may affec
193 Thus, increasing numbers of species in many biomes may be at risk as heat-wave events become more se
194 relations among traits observed in different biomes; models lacking these details would behave poorly
195 ess within most biomes (especially grassland biomes), most biodiversity hotspots, and even some wilde
196 Replication cohorts included additional BioMe (n = 1,623), Vanderbilt BioVU (n = 1,809), and Nor
197 this varies considerably within this diverse biome; N deposition explains a much smaller proportion o
199 a 4000-km climate transect in two grassland biomes of China, the Inner Mongolian temperate grassland
200 n dioxide with the atmosphere than any other biome on Earth, and thus play a disproportionate role in
201 t (TRF) is the most species-rich terrestrial biome on Earth, harbouring just under half of the world'
202 Atacama Desert is the most extreme non-polar biome on Earth, the core region of which is considered t
203 -sea ecosystems, which represent the largest biome on Earth, viruses have a recognised key ecological
206 served in the tropics, with the most diverse biome on the planet treated as a single type in models.
207 ern mangroves are among the most carbon-rich biomes on Earth, but their long-term (>/=10(6) years) im
208 e these results to the whole Atlantic Forest biome, one of the most disturbed biodiversity hotspots.
209 agnitude of the response depending on forest biomes or between angiosperms and gymnosperms or evergre
211 Here, we ask whether the distribution of biomes or range position better reflects spatial variati
212 stimates, which postulated a dry (succulent) biome origin according to the Tethys Seaway hypothesis,
213 ersification suggests that the boreal forest biome originated via genetic coevolution of above- and b
214 findings are generalizable across the tundra biome, our results indicate that consistency and caution
215 tus of present-day species, communities, and biomes over the last few decades to millennia and on the
217 elled as a function of drought, temperature, biomes, phylogenetic and functional groups and functiona
219 -annual variability patterns of European Net Biome Productivity (NBP) are linked to anomalies in heat
220 ospheric transport model prescribed with net biome productivity (NBP) from an ensemble of nine terres
222 British Heart Foundation, European Community Biomed Programme, Australian National Health and Medical
223 Tropical savannas are a globally extensive biome prone to rapid vegetation change in response to ch
224 r research gaps were revealed, with tropical biomes, protists, and soil macrofauna being especially o
225 dicate that subtropical and temperate forest biomes provide the highest carrying capacity for hunter-
226 piration rates at plot scales within certain biomes, quantitative frameworks for evaluating the relat
227 rimary production/evapotranspiration) across biomes ranging from grassland to forest that indicates a
228 e residence time (tau'E) was stable for each biome, ranging from 12 to 53.7 years for forest biomes a
230 viral nucleic acid sequences from different biomes, relies on several concentration, purification, e
232 scribe a modification of digital karyotyping-biome representational in silico karyotyping (BRISK)-as
233 d a representational deep-sequencing method (biome representational in silico karyotyping [BRiSK]) we
237 lost by fire, relative to both ecosystem and biome-scale fluxes, demonstrates that a climate-driven i
242 litter decomposition rates at the global and biome scales, and to assess how climate, litter quality
243 obtained at eddy-flux sites covering diverse biomes, setting the stage for future investigations of t
245 h lack of fuel and potentially driving local biome shifts from fynbos shrubland to nonburning semides
248 s of habitat intactness and vulnerability to biome shifts, using multiple measures of habitat intactn
250 arameters analyzed and across different land biomes, showing that the response of vegetation to droug
251 re has been largely absent from most of this biome since the early Holocene epoch, but its frequency
252 l rainforest families have characterized the biome since the Paleocene, maintaining their importance
253 Rs in global models; however, within certain biomes soil moisture and soil carbon emerge as dominant
254 t changes in environmental conditions (e.g., biomes), spatial variation in vulnerability to extirpati
255 Our results advocate for the inclusion of biome-specific soil fauna effects on litter decompositio
256 ced forest die-off is widespread in multiple biomes, strongly affecting the species composition, func
258 vation attention in the Andes has focused on biomes such as rain forest, cloud forest, and paramo, wh
259 temperature change is lowest in mountainous biomes such as tropical and subtropical coniferous fores
261 mily, testing whether they originated in dry biomes surrounding the Tethys Seaway as currently hypoth
263 smell allowed the turkey vulture to colonize biomes that are suboptimal for scavenging birds and beco
264 e in soil and sediment-two underinvestigated biomes that combined account for only approximately 2.5%
266 extensively studied across a broad range of biomes, there is surprisingly little consensus on how th
268 as been no comparative study across tropical biomes to determine rates of forest re-growth, and how t
269 We evaluated the response of the Earth land biomes to drought by correlating a drought index with th
272 on rates between biomes, from climate-driven biomes to those where climate effects were mediated by c
273 st flammable ecoregions of the boreal forest biome, to infer causes and consequences of fire regime c
274 PsychARTICLES, Web Of Science, EBM Reviews, BioMed, TRIP, ERIC, SCOPUS (January 2000-April 2011) was
276 factors tested in these analyses, including biome type, dispersal ability, and elevation preference.
277 crops and forests and substitution of these biome types for ethanol production implies trade-offs.
278 eal, conifer, deciduous, and tropical forest biomes using the LIDET-provided climatic decomposition i
279 es into the CABLE model decreased Xss in all biomes via reduced NPP (e.g., -12.1% in shrub land) or d
280 ehensive database for 231 species spanning 7 biomes, we demonstrate that temperature-dependent increa
282 , spanning 44 countries and most terrestrial biomes, we reveal a globally consistent positive concave
283 t has been statistically grouped into palaeo-biomes, we show a more transitional nature of terrestria
285 s located along the limits of the rainforest biome were significantly associated with forest losses w
289 protect forest fragments, especially within biomes where contiguous forest cover has diminished dram
290 onger growing season, especially in years or biomes where water is a limiting factor, is not due to w
291 imal populations throughout many terrestrial biomes, whereas temperature explained little variation.
292 on agricultural lands in the tropical forest biome, wherein lies the greatest potential to conserve o
293 cover across Central America, stratified by biomes, which we related to socioeconomic variables asso
294 llaboration between researchers of disparate biomes who recognize common patterns in shared data.
295 studies by searching MEDLINE, Embase, Pascal Biomed, WHOLIS, and African Index Medicus databases for
298 es of similar magnitude were observed across biomes with no apparent effect on tree growth raises the
299 icators of ancient precipitation and PFT (or biome) with modern Delta(leaf) patterns has potential to
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