ライフサイエンスコーパス: biodiversity

1 igating climate change and protecting Arctic biodiversity.

2 ges to our expanding understanding of marine biodiversity.

3 l, and biological factors thought to promote biodiversity.

4 ole of regional and local factors in driving biodiversity.

5 world will have profound impacts on mountain biodiversity.

6 d forests represent vital refugia for global biodiversity.

7 ochemical cycling, higher trophic levels and biodiversity.

8 f research into the mechanisms that maintain biodiversity.

9 mate change) degrades habitats and threatens biodiversity.

10 species, particularly in regions having high biodiversity.

11 tions and preserve much of Earth's remaining biodiversity.

12 ising policies to manage tropical carbon and biodiversity.

13 genic chytrids and prevent incipient loss of biodiversity.

14 sment of pesticides fails to protect aquatic biodiversity.

15 re ecologically destructive and can threaten biodiversity.

16 ly associated with negative consequences for biodiversity.

17 n has had severe consequences for vertebrate biodiversity.

18 consumption leads to considerable losses of biodiversity.

19 and directing climate mitigation actions for biodiversity.

20 earch skills and an unparalleled exposure to biodiversity.

21 to reveal key impacts on climate, water and biodiversity.

22 teractions, exacerbating negative impacts on biodiversity.

23 by a drastic reduction in local invertebrate biodiversity.

24 ing and assessment of the multiple facets of biodiversity.

25 their strategic value in safeguarding native biodiversity.

26 Small streams are important refuges for biodiversity.

27 agmentation have impacted global Phanerozoic biodiversity.

28 and protecting rare species, and estimating biodiversity.

29 n the U.S., which is a hotspot of salamander biodiversity.

30 role in the long-term maintenance of global biodiversity.

31 e considered in strategies to protect global biodiversity.

32 y could have other effects that enrich urban biodiversity.

33 o identify meaningful temporal baselines for biodiversity.

34 representative of damage to human health and biodiversity.

35 rural fisher livelihoods and flooded forest biodiversity.

36 rts to monitor and protect freshwater mussel biodiversity.

37 nd mitigate the impacts of climate change on biodiversity.

38 re a major threat to small streams and their biodiversity.

39 fy actions to enhance future conservation of biodiversity.

40 tely important for global carbon storage and biodiversity.

41 using it to investigate potential drivers of biodiversity.

42 n acknowledged to play a key role in shaping biodiversity.

43 ies are the most important threats to global biodiversity.

44 scale directly to the geographic gradient in biodiversity.

45 logical traps with profound consequences for biodiversity [4-6].

46 imately shifted the relative partitioning of biodiversity across time and space.

47 smal-habitat relationships, maintain natural biodiversity, advance spatial ecology, and facilitate ef

48 Our sampling of fish biodiversity and aquatic habitat along ten 3-km sites wi

49 major role in the development of theories of biodiversity and biogeography.

50 The benefits of land sparing for both biodiversity and carbon storage suggest that safeguardin

51 Tropical forests are global centres of biodiversity and carbon storage.

52 sive forest loss, with associated effects on biodiversity and carbon-cycle feedbacks to climate chang

53 arine refugia using in situ data for pelagic biodiversity and climatically sensitive areas can help g

54 ompetitive network is an important driver of biodiversity and coexistence in natural communities.

55 e amplicon data were more robust across both biodiversity and community ecology analyses at different

56 shifts for native species, patterns of local biodiversity and community structure in high latitude ec

57 observed positive correlation between global biodiversity and continental fragmentation is not readil

58 Loss of biodiversity and degradation of ecosystem services from

59 Shifts in biodiversity and ecological processes in stream ecosyste

60 mediate impacts of anthropogenic warming on biodiversity and ecosystem function across all ecologica

61 ervational and experimental field studies of biodiversity and ecosystem function.

62 The relationship between biodiversity and ecosystem functioning (BEF) is most oft

63 e will determine the extent to which Earth's biodiversity and ecosystem functioning can be maintained

64 ted elsewhere, but ecological impacts on the biodiversity and ecosystem functioning of bivalve-domina

65 ests and contribute to worldwide declines in biodiversity and ecosystem functions.

66 Structural complexity strongly influences biodiversity and ecosystem productivity.

67 -habitat connectivity to maintain gene flow, biodiversity and ecosystem resilience.

68 Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services (IPBES) recognize th

69 0% of cropland with prairie strips increased biodiversity and ecosystem services with minimal impacts

70 in mitigating climate change and protecting biodiversity and ecosystem services.

71 may seriously compromise the conservation of biodiversity and ecosystem services.

72 ably, probably as a result of a reduction in biodiversity and fertility with depth.

73 s in conservation efforts addressing aquatic biodiversity and fishery resources in the central Amazon

74 e highlight the need to: better document the biodiversity and functional roles of mountain glacier mi

75 ldwide, to quantify the interim reduction of biodiversity and functions occurring during the recovery

76 portant to estimate any resulting deficit in biodiversity and functions.

77 f distinctive hydrology which support unique biodiversity and globally significant stores of soil car

78 d areas (PAs) are intended to provide native biodiversity and habitats with a refuge against the impa

79 plex and critically important to terrestrial biodiversity and human civilization, but impacts of vira

80 While invasive species often threaten biodiversity and human well-being, their potential to en

81 hysical processes influencing persistence of biodiversity and identify a conservation network resilie

82 eDNA to examine temporal shifts in ecosystem biodiversity and in an ecologically important group of m

83 d opportunities to further unravel bacterial biodiversity and its worldwide role from human health to

84 cloud forests (TMCFs) harbour high levels of biodiversity and large carbon stocks.

85 e.g., amino acids and fatty acids), and both biodiversity and life history traits.

86 en suggested as causes of global patterns of biodiversity and phenotypic variation.

87 gap given ongoing human-caused alteration of biodiversity and plant community structure at the global

88 h this practice may have negative effects on biodiversity and populations of individual species, it m

89 alls in marine environments can harbour high biodiversity and provide natural protection from bottom-

90 is restricted to a small fraction of insect biodiversity and to a recent evolutionary timeframe, the

91 ctors including habitat degradation, loss of biodiversity and wildlife population reductions resultin

92 Urban centers are important foci for plant biodiversity and yet widespread planting of wildflower g

93 impacts on carbon and hydrological cycling, biodiversity, and ecosystem services.

94 g brings another dimension to exploration of biodiversity, and large-scale mitochondrial DNA cytochro

95 ationships among microbial metal resistance, biodiversity, and metal sorption capacity.

96 ow tropical cyclones currently affect marine biodiversity, and pelagic species in particular, is limi

97 also explored in the context of abiogenesis, biodiversity, and searches for future exoplanets.

98 mental covariates, increases in biomass with biodiversity are stronger in nature than has previously

99 reas will coalesce, and while the effects on biodiversity are uncertain, we hypothesize that they cou

100 logical invasions can have strong impacts on biodiversity as well as ecosystem functioning.

101 e is a primary driver of the distribution of biodiversity as well as of ecosystem boundaries.

102 a primary threat to species persistence and biodiversity at a global scale.

103 ficant and continuous increases in all three biodiversity attributes until ca. 2000, followed by a sl

104 We studied wildflower viewing, a key biodiversity-based CES in amenity-based landscapes, in S

105 ng sustainable food production, by promoting biodiversity beneficial to agricultural production throu

106 tent differences in relative partitioning of biodiversity between time and space across habitats.

107 o forecast the improvement that any proposed biodiversity budget would achieve under various scenario

108 ed to boost food production while protecting biodiversity, but alone these proposals are unlikely to

109 esized that plate tectonics regulates global biodiversity by changing the geographic arrangement of c

110 een offers opportunities for the increase of biodiversity by facilitating challenging conditions for

111 t Goals of human development and maintaining biodiversity, by predicting the dynamic changes in conse

112 gi facilitated a better understanding of how biodiversity can be jointly shaped by large-scale histor

113 process since microbial metal resistance and biodiversity can play a direct role in the bioremediatio

114 Our results highlight the positive role biodiversity can play in ecosystem restoration and call

115 Understanding global patterns of biodiversity change is crucial for conservation research

116 ting knowledge of environmental degradation, biodiversity change, and ecosystem processes across larg

117 t a global level limits our understanding of biodiversity changes and their local-scale drivers.

118 In natural systems, biodiversity changes are often part of a bigger communit

119 We also show that biodiversity changes in signatory countries can be predi

120 at an unprecedented rate through changes in biodiversity, climate, nitrogen cycle, and land use.

121 roblem while providing greater potential for biodiversity conservation and fishery rebuilding if over

122 ped CAFC maps aim to facilitate decisions on biodiversity conservation and reforestation programs in

123 Worldwide, enormous potential for biodiversity conservation can be realized by upgrading e

124 The situation is a lost opportunity for biodiversity conservation globally.

125 include impacts on human health, culture and biodiversity conservation more generally.

126 Biodiversity conservation projects confront immediate an

127 Biodiversity conservation requires reliable species asse

128 ty to be measured over time, the targets for biodiversity conservation to be defined and conservation

129 one of the highest returns on investment for biodiversity conservation worldwide.

130 cations for fields as divergent as medicine, biodiversity conservation, agriculture and space explora

131 rained by food security, fiber security, and biodiversity conservation-is 23.8 petagrams of CO2 equiv

132 ning protected areas (PAs) are key tools for biodiversity conservation.

133 nown repercussions for local communities and biodiversity conservation.

134 ols to advance these goals for multi-faceted biodiversity conservation.

135 As global biodiversity continues to decline steeply, it is becomin

136 The ongoing biodiversity crisis increases the importance and urgency

137 nderestimations of the extent of the current biodiversity crisis.

138 Biodiversity damage was mainly related to the energy and

139 mal timing of decisions balances the rate of biodiversity decline (e.g., the relaxation of extinction

140 s desperately needed to fight against global biodiversity declines resulting from human impacts.

141 efforts to protect habitat given continuing biodiversity declines.

142 s, and secondarily driven by other important biodiversity drivers such as climate, soil spatial heter

143 uilding more complete and accurate models of biodiversity dynamics that can inform ecological and evo

144 Pests are a global threat to biodiversity, ecosystem function, and human health.

145 knowledge gap, we tested whether a number of biodiversity, ecosystem functions and ecosystem conditio

146 ost-extinction compensatory mechanisms alter biodiversity-ecosystem function relations following non-

147 A major gap in our understanding of biodiversity-ecosystem function relationships concerns t

148 logical stoichiometry, metabolic theory, and biodiversity-ecosystem function relationships), all in t

149 This work supports a mutualist biodiversity-ecosystem functioning relationship, highlig

150 y of forest ecosystems at global scale using biodiversity-ecosystem functioning relationships.

151 Biodiversity enhances many of nature's benefits to peopl

152 reatens the sustainability of coastal marine biodiversity, especially in tropical developing countrie

153 ities, and priorities for the different bird biodiversity facets are more similar than those of mamma

154 Soil biodiversity, fertility and plant productivity are stron

155 positive feedback relationships between soil biodiversity, fertility and plant productivity are unive

156 r soil layer, the relationships between soil biodiversity, fertility and plant productivity weaken co

157 uld potentially break the links between soil biodiversity-fertility and/or fertility-plant productivi

158 diversity losses due to GHG emissions in the biodiversity footprint increases with income; (iii) food

159 de their territorial boundaries; and (v) the biodiversity footprint per dollar consumed is lower for

160 sumption-based biodiversity losses, in short biodiversity footprint, for 45 countries and world regio

161 ngs highlight the importance of surface soil biodiversity for soil fertility, and suggest that any lo

162 sitively correlated with the state of global biodiversity for tens of millions of years afterward.

163 Our findings indicate that the generalized biodiversity-function relation curve, as derived from mu

164 tant implications for the marine-terrestrial biodiversity gradient, and studies of biodiversity gradi

165 strial biodiversity gradient, and studies of biodiversity gradients in general.

166 rable manipulation intensity was as follows: biodiversity>grazing>precipitation>N.

167 s follows: precipitation>grazing>temperature>biodiversity>N.

168 er filtration, flood buffering, soil health, biodiversity habitat, and enhanced climate resilience.

169 change the availability and connectivity of biodiversity habitat.

170 evels of exclusive and critically endangered biodiversity harboured by current patches of the Afromon

171 The Coral Triangle is a hotspot for marine biodiversity held in its coral reefs, seagrass meadows,

172 nd sites located in the Brazilian Cerrado, a biodiversity hotspot.

173 est of Brazil are two of the most fragmented biodiversity hotspots.

174 Montane environments around the globe are biodiversity 'hotspots' and important reservoirs of gene

175 are expressed in terms of climate change and biodiversity impacts due to water and land use.

176 highlights the importance, in evaluating the biodiversity impacts of land use, of measuring populatio

177 here aimed at broadly capturing the enormous biodiversity in antibody profiles that may emerge follow

178 nded as the most appropriate measure of food biodiversity in diets.

179 facilitate effective conservation of native biodiversity in human-altered ecosystems.

180 ass production, and suggest that the role of biodiversity in maintaining productive ecosystems should

181 This biodiversity in response makes future ecosystems predict

182 e, however, little is known about meiofaunal biodiversity in sediment communities, which are a vital

183 The importance of biodiversity in supporting ecosystem functioning is gene

184 widespread predatory mollusc that structures biodiversity in temperate rocky shores.

185 sults show that almost all of the meiofaunal biodiversity in the benthic habitat has yet to be charac

186 Conserving native biodiversity in the face of human- and climate-related i

187 , our results show climate change impacts on biodiversity in the hyperdiverse Cape Floristic Region a

188 Theory predicts that higher biodiversity in the tropics is maintained by specialized

189 egulators to conserve and enhance freshwater biodiversity in urbanized landscapes whilst also facilit

190 genic stressors on hydrologic alteration and biodiversity in US streams and isolate the impacts stemm

191 Temporal baselines are needed for biodiversity, in order for the change in biodiversity to

192 ldflower communities vary with components of biodiversity, including species richness?; (ii) How do a

193 Effects of biodiversity indicators on productivity were comparable

194 es, we have little understanding of how this biodiversity influences the biological carbon pump other

195 gnparser) is a fast, high precision tool for biodiversity informaticians and biologists working with

196 bined tree distribution data from the Global Biodiversity Information Facility, EUFORGEN, and forest

197 Limited biodiversity information is widely recognized as a major

198 stand the causes of cycle gain and loss, how biodiversity interacts with population cycling, and how

199 lity and we hypothesized that this may alter biodiversity-invasion relationships.

200 lternatively, recent evidence indicates that biodiversity is best conserved by minimizing human intru

201 ation of phytoplankton species and microbial biodiversity is necessary to assess water ecosystem heal

202 ower gardens in cities to sustain pollinator biodiversity is on the rise, without full consideration

203 wo fundamental axes, space and time, but how biodiversity is partitioned along both axes is not well

204 onse of ANPP to changes in precipitation and biodiversity is saturating, so we expected larger effect

205 etween the stability of ecosystems and their biodiversity is still not well understood.

206 The hazard plastic debris poses to biodiversity is well established, but mitigation and pla

207 e species, a significant threat to worldwide biodiversity, is predicted to increase due to climate-in

208 ) is the most commonly assessed attribute of biodiversity, it misses the potential functional or phyl

209 eiofauna) using metabarcoding to investigate biodiversity levels in sediment communities of the Antar

210 recent past) and are expected to drive major biodiversity loss and changes in ecosystem functioning.

211 inability challenges such as climate change, biodiversity loss and food security, improving our under

212 Anthropogenic landscapes are associated with biodiversity loss and large shifts in species compositio

213 that sociopolitical instability can lead to biodiversity loss and undermine the benefit of existing

214 al average of 40%; (iv) more than 50% of the biodiversity loss associated with consumption in develop

215 etheless, global goals to reduce the rate of biodiversity loss have mostly not been achieved.

216 Consensus has been reached that global biodiversity loss impairs ecosystem functioning and the

217 quantify how conservation investment reduced biodiversity loss in 109 countries (signatories to the C

218 consumption is the most important driver of biodiversity loss in most of the countries and regions,

219 Global biodiversity loss is a critical environmental crisis, ye

220 Halting global biodiversity loss is central to the Convention on Biolog

221 nmental changes are accelerating the rate of biodiversity loss on Earth.

222 Our results showed that (i) the biodiversity loss per citizen shows large variations amo

223 experiments have collectively suggested that biodiversity loss reduces ecosystem productivity and sta

224 Biodiversity loss substantially diminishes several ecosy

225 lar intensity of manipulation, the effect of biodiversity loss was 4.0, 3.6, and 1.5, times larger th

226 f nutrient excretion would be 28% greater if biodiversity loss was random or 84% greater if there wer

227 uilding on these lessons to turn the tide of biodiversity loss will require bold and innovative actio

228 Hunting is a major driver of biodiversity loss, but a systematic large-scale estimate

229 Global challenges such as food security, biodiversity loss, water scarcity and human health are a

230 intensification is a leading cause of global biodiversity loss, which can reduce the provisioning of

231 ring ecosystem structure and contributing to biodiversity loss.

232 lone these proposals are unlikely to staunch biodiversity loss.

233 r-capita income increases; (ii) the share of biodiversity losses due to GHG emissions in the biodiver

234 and services by presenting consumption-based biodiversity losses, in short biodiversity footprint, fo

235 obal environmental change, urbanization, and biodiversity losses.

236 tion targets aimed at restoring or reversing biodiversity losses.

237 riencing land-use changes and where wildlife biodiversity (mammal species richness) is high.

238 r limitation increases under climate change, biodiversity may become even more important to support h

239 a processing methods can skew sequence-based biodiversity measurements from corresponding relative bi

240 ed as a major factor shaping plant community biodiversity, metabolic processes, and ecosystem dynamic

241 tly link desired conservation objectives and biodiversity metrics.

242 Setting temporal baselines from biodiversity monitoring data would therefore underestima

243 temporal baselines that could be drawn from biodiversity monitoring schemes in Europe and compare th

244 Most biodiversity monitoring schemes were initiated late in t

245 additional research efforts beyond standard biodiversity monitoring to reconstruct the impacts of ma

246 sults show that effects of climate change on biodiversity must be analyzed in the context of historic

247 onding to the influence of climate change on biodiversity must consider a broad array of ecological p

248 vide novel evidence of several thresholds in biodiversity (namely species richness of ectomycorrhizal

249 Antarctic terrestrial biodiversity occurs almost exclusively in ice-free areas

250 n, evolution, and ecology of the exceptional biodiversity of Amazonian forests.

251 ins of oak diversity is key to understanding biodiversity of northern temperate forests.

252 he study contributes to our understanding of biodiversity on the QTP.

253 Different facets of biodiversity other than species numbers are increasingly

254 Similar to findings for terrestrial biodiversity, our data suggest that the marine speciatio

255 nd apparently pristine as the Antarctic, the biodiversity outlook is similar to that for the rest of

256 zation levels provide a truncated picture of biodiversity over time.

257 ate variability is more important in shaping biodiversity patterns rather than gradual changes in lon

258 maximize basic representation of the global biodiversity pool than to maximize local diversity.

259 is optimal, and uncertainty surrounding how biodiversity produces services makes it optimal to prote

260 ggest that safeguarding natural habitats for biodiversity protection and carbon storage alongside pro

261 Our work shows that large gains in biodiversity protection are possible, while also highlig

262 How much biodiversity protection would result from this modified

263 , quantitative and comprehensive approach to biodiversity protection, most insights are still focused

264 ergy concerns related to climate mitigation, biodiversity, reactive nitrogen loss, and crop water use

265 Consideration of these effects of biodiversity redistribution is critical yet lacking in m

266 g income to hedge financial risk, increasing biodiversity, reducing soil erosion, and improving nutri

267 advancements in metagenomics, much of their biodiversity remains uncharacterized.

268 Effective conservation of freshwater biodiversity requires spatially explicit investigations

269 d global-change biology is to understand why biodiversity responds differently to similar environment

270 Contingent biodiversity responses may depend on how disturbance and

271 s is necessary in order to properly describe biodiversity responses to climate change rather than the

272 role in mediating biotic homogenisation and biodiversity responses to environmental change.

273 ey as a model for engaging undergraduates in biodiversity science.

274 ights are still focused on a single facet of biodiversity-species.

275 o measure the drivers underpinning ecosystem biodiversity, status and trajectory.

276 nue for standardized citizen science on bird biodiversity surveys worldwide.

277 conservation across three key dimensions of biodiversity-taxonomic, phylogenetic, and traits-and (ii

278 nown about its effect on other components of biodiversity that may be at risk.

279 of the most fundamental phenomena in nature: biodiversity that seems to be excluded by the principle

280 ferences and consider multiple dimensions of biodiversity that underpin CES supply.

281 ic habitat types disproportionately increase biodiversity, these keystones should be incorporated int

282 ntal crisis, yet the lack of spatial data on biodiversity threats has hindered conservation strategie

283 ribute to both local livelihoods and protect biodiversity throughout Myanmar during economic growth.

284 ive symmetry-breaking mechanisms can promote biodiversity to a broader extent than previously thought

285 for biodiversity, in order for the change in biodiversity to be measured over time, the targets for b

286 for the processes that generate and maintain biodiversity to continue.

287 eneralize responses of this major feature of biodiversity to future environmental change.

288 our abilities to make predictions on future biodiversity under any range of scenarios.

289 ntial for realistic forecasts of patterns of biodiversity under climate change, with implications for

290 conservation would facilitate persistence of biodiversity under climate change.

291 algorithms, previous studies that quantified biodiversity using such bioinformatic tools should be vi

292 of a nature connection, given disparities in biodiversity values of private gardens in relation to so

293 es in their neighborhoods in relation to the biodiversity values of those spaces, in three New Zealan

294 Using birds as an indicator taxon of wetland biodiversity, we model time-series abundance data for 46

295 Californian grassland, a hotspot for global biodiversity, we used a seed vacuum to increase dispersa

296 bitat has yet to be characterised, levels of biodiversity were higher than expected and similar to te

297 dequate responses to avert further losses of biodiversity when population and incomes increase.

298 ing key insight as to how and when losses in biodiversity will impact ecosystem function.

299 ing interest in the historical generation of biodiversity within this region.

300 ing opinion of the previous two decades that biodiversity would have rare or weak effects in nature,