ライフサイエンスコーパス: plant community

1 nance of a competitive annual species in the plant community.

2 tity of nutritional resources from a diverse plant community.

3 xperiencing competition from the surrounding plant community.

4 er warming but did not respond to changes in plant community.

5 anaerobic decomposition, and changes in the plant community.

6 number of species changing phenology in this plant community.

7 nd rising atmospheric CO(2) concentration on plant communities.

8 proaching the higher levels seen in restored plant communities.

9 ed microorganisms, soil thermal regimes, and plant communities.

10 nt on the ecological functioning of dominant plant communities.

11 ly shape the composition and architecture of plant communities.

12 g stable pollination to agriculture and wild plant communities.

13 died, yet may have important implications in plant communities.

14 ibutions and patterns of rarity in worldwide plant communities.

15 ily, warming-induced changes in forest floor plant communities.

16 changes in response to the transformation of plant communities.

17 erformance of exotics and natives in invaded plant communities.

18 vulnerability signatures across the region's plant communities.

19 ants to understand their role in structuring plant communities.

20 il N cycle and ecosystem functions in extant plant communities.

21 , and the development of, and/or changes in, plant communities.

22 es, and the proportion of exotics in invaded plant communities.

23 the relationships between soil microbial and plant communities.

24 n genotypes) affect diversity or dynamics in plant communities.

25 ng a dataset of 459 woody and 589 herbaceous plant communities.

26 mote species diversity and seed dispersal in plant communities.

27 wing the maintenance of species diversity in plant communities.

28 ich likely shape ecological interactions and plant communities.

29 ion, and the phylogenetic diversification of plant communities.

30 genotype-specific pathogens in multispecies plant communities.

31 tute an excellent resource for the algal and plant communities.

32 alter the species compositions of freshwater plant communities.

33 narrowing of interactions to a subset of the plant community accompanies pollinator niche specialisat

34 s and species richness for temperate wetland plant communities across continents, latitudes, and migr

35 es of 22 factorial experiments in herbaceous plant communities across Europe and North America, we sh

36 We used species-level abundance data from 62 plant communities across five continents to assess mecha

37 , based on an analysis of NPP for 1247 woody plant communities across global climate gradients, that

38 ovide a synthesis of 727 tests of the SGH in plant communities across the globe to examine its genera

39 transplanted alpine plant species and intact plant communities along a climate gradient in the Swiss

40 Here, we reciprocally transfer plant communities along an elevation gradient to investi

41 icrobial communities, soil temperatures, and plant communities also contributing to this reduction.

42 Global change is exerting a major effect on plant communities, altering their potential capacity for

43 Fungi play an important role in plant communities and ecosystem function.

44 e change will alter FLSs and thereby reshape plant communities and ecosystems.

45 importance of allelopathy in shaping natural plant communities and for agricultural production, the u

46 pathogens have both in structuring tropical plant communities and in maintaining their remarkable di

47 been central to the evolutionary assembly of plant communities and plant-nutrient feedbacks at the sc

48 g effects on the thermophilization in forest plant communities and propose an alternative way to anal

49 g emergence timing is crucial in competitive plant communities and so contributes to species fitness.

50 microbial communities, along with changes in plant communities and soil carbon (C) and nitrogen (N) d

51 irect and indirect temperature controls over plant communities and soil properties in seven contrasti

52 tical role in determining warming effects on plant communities and species invasions.

53 e connection between functional diversity of plant communities and the critical ecosystem service of

54 to infer the roles of mutualistic animals in plant communities and to predict the effect of species'

55 mass and net primary production (NPP) at the plant community and functional type levels.

56 a(2)H values in paleoapplications; when both plant community and growth form are known, this study al

57 Plant community and soil properties provide a major cont

58 he most visible effects of climate change on plant communities, and has been especially pronounced in

59 Yet, consumers can strongly affect plant communities, and means for linking consumer effect

60 in, carbon dioxide enrichment in terrestrial plant communities, and nitrogen deposition.

61 anges in growth patterns in alpine grassland plant communities, and suggest that earlier phenology an

62 ammalian herbivores (LMH) strongly influence plant communities, and these effects can propagate indir

63 ve abundance of a species across a grassland plant community, and that this rare-species advantage ha

64 insight into the effects of leaf wetting on plant, community, and ecosystem function.

65 Although many plant communities are invaded by multiple nonnative spec

66 iring degraded soil conditions and restoring plant communities are likely necessary for restoring gra

67 Plant communities are not stable over time and biologica

68 mophilization and the climatic lag in forest plant communities are primarily controlled by microclima

69 Human influences are reshaping plant communities around the world through both extincti

70 regimes are creating novel environments for plant communities around the world.

71 mate change is expected to have an impact on plant communities as increased temperatures are expected

72 y between the montane and pre-montane forest plant communities, as well as among species within a for

73 We added a pulse of (15) N to grassland plant communities assembled to represent a range of comm

74 raits to help uncover the mechanisms driving plant community assembly.

75 nfluence global patterns of biodiversity and plant community assembly.

76 reserved in a soil horizon resolve different plant communities at meter scales across a contiguous 25

77 changes in the diversity and composition of plant communities at the local scale cause ecosystem fun

78 Shrubs facilitated the annual plant community at all levels of soil moisture through r

79 e, we tested under glasshouse conditions how plant community attributes, including variations in the

80 ng been recognized as a major factor shaping plant community biodiversity, metabolic processes, and e

81 Ecological theory and evidence suggest that plant community biomass and composition may often be joi

82 indings point to the co-limitation of alpine plant community biomass and structure by nitrogen and CO

83 d precipitation on the temporal stability of plant community biomass in an alpine grassland located o

84 ophic interactions proportionately decreased plant community biomass mean and variability over the co

85 aving a dramatic impact on marine animal and plant communities but little is known of its influence o

86 ude that the initial composition of not only plant communities, but also soil communities has a long-

87 Insect herbivory is pervasive in plant communities, but its impact on microbial plant col

88 a global threat to the biodiversity of many plant communities, but its impacts on grassland soil see

89 Drought can cause major damage to plant communities, but species damage thresholds and pos

90 ass-specific flux rates in the low-diversity plant communities by altering plant species composition

91 cits short- and long-term changes in coastal plant communities by altering the physical conditions th

92 nts may determine abundance and diversity in plant communities by influencing fitness and competitive

93 icrobes are thought to maintain diversity in plant communities by specializing on particular species,

94 mechanism of shrub facilitation on an annual plant community can change with precipitation extremes i

95 esponding to rapid acidophilic to halophilic plant community change and a carbon accumulation decline

96 global trait-space, informing prediction of plant community change in a warming world.

97 there may be generality in the mechanisms of plant community change with N enrichment.

98 feedbacks from other limiting resources and plant community change, which remain poorly understood f

99 ations increased NPP and soil C storage, but plant community changes and GHG emissions decreased, and

100 es distribution models) rarely consider that plant community changes could substantially lag behind c

101 We measured changes in perennial plant community characteristics (cover, species richness

102 and bacteria in the nectar of a coflowering plant community, characterize the volatiles produced by

103 ts also show that incorporating data on both plant community compartments will further our understand

104 of native species at all sites, we measured plant community composition (i.e., cover, richness, and

105 sts and (b) simulating both productivity and plant community composition accurately without physicall

106 inundation, disturbance and dispersal shape plant community composition along key environmental grad

107 with SLR are primarily mediated by shifts in plant community composition and associated plant traits

108 ity, linking changes in both to stability in plant community composition and biomass production.

109 ts and that temperature is a major driver of plant community composition and change.

110 e are expected to have widespread effects on plant community composition and diversity in coming deca

111 nder different nutrient regimes, influencing plant community composition and ecosystem dynamics.

112 cies, and (iii) assessed postfire understory plant community composition and flammability.

113 ldwide and (2) the emergent consequences for plant community composition and land biogeochemical cycl

114 lue of the ecosystem is largely dependent on plant community composition and the relative abundance o

115 re selected to be highly similar in terms of plant community composition and tidal influence.

116 Soil carbon (C) pools and plant community composition are regulated by nitrogen (N

117 ches by comparing the degree to which tundra plant community composition changes (i) in response to i

118 This shift in plant community composition from grassland to shrub thic

119 We analyzed changes in plant community composition from repeat sampling (85 pla

120 Here, we show that plant community composition in 996 Swedish landscapes ha

121 nd plant seeds alter soil-borne nematode and plant community composition in semi-natural grassland fo

122 Our results show that plant community composition is a significant modulator o

123 vated atmospheric CO(2), eutrophication, and plant community composition on CH(4) emissions from an e

124 as stabilized under deepened winter snow and plant community composition remained unchanged.

125 intense droughts, which can drive changes in plant community composition through a variety of mechani

126 is a high-resolution tool useful for linking plant community composition to below-ground soil microbi

127 mate change, may change soil functioning and plant community composition via the modification of plan

128 Plant community composition was impacted by both asymmet

129 rannual precipitation, while the response of plant community composition was more sensitive to experi

130 ng and the resultant drying of soils altered plant community composition, decreased native diversity,

131 closer to that of the old growth forest; (3) Plant community composition, edaphic parameters, and geo

132 an populations may be locally adapted to the plant community composition, elevation, local climate, a

133 ade plot-level measurements of CO2 exchange, plant community composition, foliar nitrogen concentrati

134 However, barring large shifts in plant community composition, future increases in old soi

135 he Arctic is already experiencing changes in plant community composition, so understanding the contri

136 ion and surface fires also connected through plant community composition, via the species' traits?

137 ve drought stress and had minimal effects on plant community composition.

138 lant interactions might interact to regulate plant community composition.

139 predicting successional dynamics and future plant community composition.

140 ces, and ecological processes that depend on plant community composition.

141 nvironmental nutrient supplies can determine plant community composition.

142 asion, our results indicate clear changes in plant community composition: cover of graminoids and non

143 directly impact seed dispersal patterns and plant community composition; however, we know less about

144 wide range of nutrient inputs, soil pH, and plant community compositions during the last century.

145 In a plant community consisting of seven plant species that c

146 d litter traits among invaded and noninvaded plant communities control the magnitude and direction of

147 Large decline in plant community cover, primarily caused by the reduction

148 top-down and indirect effects of insects on plant communities depend on patterns of host use, which

149 g exotics and suppressing natives in invaded plant communities, depending on the type, frequency, and

150 ich is likely to have important feedbacks on plant community development.

151 did a worldwide test of the hypotheses that plant community divergence in antiherbivore traits resul

152 ent (NDD) recruitment capable of maintaining plant community diversity at landscape scales.

153 to the strength and scale of PSF and overall plant community diversity.

154 that had been conditioned by model grassland plant communities dominated by either slow- or fast-grow

155 ure false springs, and potentially reshaping plant community dynamics given uneven shifts in risk acr

156 ance near conspecific adults and influencing plant community dynamics on ecological and evolutionary

157 backs with respect to microbial mediation of plant community dynamics.

158 e and long-lasting effects of disturbance on plant community dynamics.

159 Most terrestrial plant communities exhibit relatively high species divers

160 Unlike monocultures, diverse plant communities favor the development of 30-150 um por

161 d temporal stability of productivity for 243 plant communities from 42 grasslands across the globe an

162 Positive interactions can buffer plant communities from abiotic stress and consumer press

163 the late Miocene coincident with a shift in plant communities from C3 to C4 grasses.

164 We surveyed paired invaded and uninvaded plant communities from three biomes.

165 Consequently, warming shifted the plant community from invader-dominated to native-dominat

166 stribution of the climatic envelopes of this plant community further, suggesting that current high-re

167 rthern California grassland with a mosaic of plant communities generated by different soil types, we

168 We used experimental wetland plant communities grown from seed banks as model systems

169 , although it is likely that the recovery of plant communities has been facilitated by the twice-year

170 Species-rich plant communities have been shown to be more productive

171 change is expected over the coming century, plant communities have on average sixfold more biomass b

172 Trait-based approaches to terrestrial plant communities have shown that functional traits can

173 The diversity of pollinating insects and the plant community have the highest predictive power for fl

174 mmunity-wide prevalence, and turnover in the plant community impacted when parasite transmission was

175 mmunity composition from repeat sampling (85 plant communities in 28 regions) and experimental warmin

176 Whether plant communities in a given region converge towards a p

177 phylogenetically paired native and nonnative plant communities in a glasshouse experiment to test div

178 forecast the impacts of multiple drivers on plant communities in an era of rapid change.

179 respiration through altering composition of plant communities in grassland ecosystems.

180 ssification to quantitative determination of plant communities in nature.

181 stimates of primary productivity from fossil plant communities in North America and Europe.

182 We suggest that the standard assumption that plant communities in remote locations are primarily shap

183 Thus, plant communities in shortgrass prairie may shift toward

184 Establishing and developing plant communities in these affected areas is crucial in

185 nerally found no effect of elevated [CO2] on plant communities in this arid ecosystem.

186 and ecosystem nitrogen, and distribution of plant communities in this brackish wetland.

187 y may be especially vulnerable to decline in plant communities in warm, water-limited regions, as int

188 deposition on a Mediterranean-type shrubland plant community in southern California from 2011 to 2016

189 nipulative field experiment in a subtropical plant community in the subsiding Mississippi River Delta

190 As global changes reorganize plant communities, invasive plants may benefit.

191 rbuscular mycorrhizal (AM) fungi covary with plant communities is clear, and many papers report nonra

192 the effects of global change on terrestrial plant communities is crucial because of the ecosystem se

193 etation that the climatic debt in understory plant communities is locally modulated by canopy bufferi

194 st how important dispersal is in structuring plant communities is nevertheless an open question becau

195 compared to interspecific trait variation in plant communities is still missing.

196 ast 75 years, and flowering phenology of the plant community is advanced in years with warmer tempera

197 cology, from the level of the fungus, at the plant community level, and to functional consequences in

198 cies abundance changes (demography) nor with plant community-level responses to long-term climate tre

199 ent (i.e. not differing from single-plant to plant-community levels) and (3) soil and microbial bioma

200 ts on plant C pools at both single-plant and plant-community levels; (2) plant C pool responses to in

201 crease or reduce evolutionary relatedness in plant communities, making it difficult to generalize res

202 ther, these results demonstrate that invaded plant communities may accumulate additional non-native s

203 ithout considering how concurrent changes in plant communities may alter such effects.

204 In peatland ecosystems, plant communities mediate a globally significant carbon

205 may be amplified by the shift toward forest plant communities more susceptible to fire-driven diebac

206 g stoichiometric convergence of ground-layer plant community nitrogen to phosphorus ratios across all

207 Here, we focus on nitrogen and ask whether plant community nitrogen uptake rate is determined (a) b

208 In contrast, plant community nitrogen uptake rate was clearly affecte

209 We found that plant community nitrogen uptake rate was unaffected by f

210 We found that plant communities of biodiversity experiments cover almo

211 ronmental policymakers as early successional plant communities of low conservation value.

212 hich human activity has impacted the natural plant communities of Madagascar is of critical and endur

213 Tropical biomes are the most diverse plant communities on Earth, and quantifying this diversi

214 ng a detailed functional description of many plant communities on Earth.

215 change may have relatively little effect on plant communities on nutrient-poor soils.

216 o 500 uL L(-1)) for eight years to grassland plant communities on soils from different landscape posi

217 ctional change may change the composition of plant communities over time.

218 ve no information about potential effects on plant community productivity and structure.

219 es and their trait compositions, with future plant communities projected to be occupied by taller pla

220 atterns in the relative importance of ITV in plant communities, providing practical guidelines for wh

221 low abundance thresholds needed to suppress plant community recovery, and much higher levels needed

222 Functional composition of the plant community regulated warming-induced increases in s

223 eriment to explore the mechanisms underlying plant community regulation on feedbacks of soil respirat

224 In experimental plant communities, relationships between biodiversity an

225 ence resource acquisition across species and plant communities remains obscure.

226 es of montane ecosystems, particularly where plant community reorganization outpaces treeline advance

227 Understanding how plant communities respond to temporal patterns of precip

228 Two sources of complexity make predicting plant community response to global change particularly c

229 Models forecasting plant community responses to global change incorporate s

230 these shifts was related to the magnitude of plant community responses to nutrient inputs.

231 nitrogen enrichment, accelerated directional plant community responses to warming, increasing the dom

232 han macroclimate warming for studying forest plant community responses to warming.

233 d landscapes, with novel ornamental and crop plant communities, result not only in changes to local c

234 ed with soil pH, mean annual temperature and plant community richness (Spearman's r: 0.77, 0.64 and -

235 In addition, soil pH and plant community richness both explained significant vari

236 viduals explain the lack of strong perennial plant community shifts after a decade of elevated [CO2].

237 osystem-level processes may be influenced by plant community shifts.

238 ulations--irrigation and drought--to dryland plant communities situated along a steep climatic gradie

239 We used a tundra plant-community-specific leaf area index (LAI) model to

240 ition, and increased winter precipitation on plant community structure and aboveground net primary pr

241 ught events could have profound influence on plant community structure and ecosystem function, and ha

242 time warming have the potential to influence plant community structure and ecosystem functions.

243 endogenous disturbance regimes in studies of plant community structure and function.

244 es have occurred in parallel with impacts on plant community structure and may have contributed to th

245 vated CO2, warming, and summer irrigation on plant community structure and productivity, linking chan

246 Herbivores are critical in determining plant community structure and the transfer of energy up

247 trade-offs, ecologists can begin to predict plant community structure at global scales.

248 human-caused alteration of biodiversity and plant community structure at the global scale.

249 In addition, herbivory modulates shifts in plant community structure caused by warming.

250 wfall will affect ecosystem productivity and plant community structure during the growing season.

251 mount of growing season rainfall will impact plant community structure in annually burned, native tal

252 erstanding the effects of elevated [CO2 ] on plant community structure is crucial to predicting ecosy

253 However, little is known about how plant community structure regulates responses of soil re

254 Parasitic plants have major impacts on plant community structure through their direct negative

255 hese significant treatment effects, ANPP and plant community structure were highly resistant to these

256 st mortality has important ramifications for plant community structure, ecosystem function, and the e

257 Soil fertility influences plant community structure, yet few studies have focused

258 ive feedbacks between limiting resources and plant community structure.

259 nally, we observed that microfibers affected plant community structure.

260 EPPs are widely used in plant community studies focused on negative density-depe

261 dels, which encode a very simplified view of plant communities, suggesting that the potential for nic

262 ent that fire-adapted species often dominate plant communities, suggesting that wildfire is an integr

263 h temperature for the local, lower elevation plant communities surrounding the experimental alpine tu

264 have more serious negative implications for plant communities than is currently assumed.

265 vaded was lawn or wooded, but the marsh-edge plant communities that developed in these two environmen

266 d use can create altered soil conditions and plant communities that persist for decades, although the

267 he severe negative effects of N pollution on plant communities that threaten the stability of populat

268 y examines the pygmy forest in California, a plant community that experiences negligible water stress

269 In most plant communities, the net effect of nitrogen enrichment

270 improvement and their extensive study by the plant community, the molecular mechanisms controlling th

271 diverse portfolio of urban green spaces and plant communities therein to facilitate complex microbia

272 In old-fields and other plant communities, these soil feedbacks appear common, f

273 ersity stabilises productivity in herbaceous plant communities through a combination of overyielding,

274 the microbial mechanism linking species-rich plant communities to a carbon cycle process of importanc

275 or cloches to examine the response of Arctic plant communities to artificially elevated temperatures.

276 nt estimates of the magnitude of response of plant communities to climate warming.

277 vated [CO2], but the response of intact arid plant communities to elevated [CO2 ] is largely unknown.

278 ay also explain why a comparable response of plant communities to reduced N inputs has yet to be obse

279 likely interact with fire-induced changes in plant communities to reshape the biodiversity in tropica

280 design allows upscaling from root anatomy to plant community to estimate the following: resource cost

281 ed biotic interactions and dispersal lags to plant community turnover along an elevational gradient f

282 modeled predictions for the distribution of plant community types in the Alaskan arctic foothills re

283 both woody encroached and nearby herbaceous plant community types.

284 rost may play an important role in affecting plant communities under climate change.

285 anding of how plant-soil feedbacks structure plant communities, underlie invasive species dynamics, o

286 Here, we reconstruct past plant communities using sedimentary ancient DNA (sedaDNA

287 Understanding how and why plant communities vary across space has long been a goal

288 ecosystem productivity of diverse grassland plant communities was more resistant, changing less duri

289 bution of the key CH4 emitting and consuming plant communities was possible from satellite, allowing

290 ith relative sea-level rise showed that this plant community was experiencing an elevation deficit (i

291 owered mean soil water content, overall this plant community was remarkably resistant to altered prec

292 Soil variables and plant communities were also assessed as proximate driver

293 k/cores, twigs, leaves/needles) of the local plant community were taken, namely silver birch (Betula

294 esistance against the effects of M. rubra on plant communities when these species coexist.

295 however, would have a massive impact on all plant communities, which are found to exhibit clear thre

296 nd, rapid glacier retreat is exposing intact plant communities whose radiocarbon dates demonstrate en

297 e, we compare data from real-world grassland plant communities with data from two of the largest and

298 In a glasshouse experiment we constructed plant communities with different levels of barley (Horde

299 the relative extent of ITV within and among plant communities worldwide, using a data set encompassi

300 onary history determined HP load size across plant communities worldwide.