ライフサイエンスコーパス: richness

1 between coral age and microbial diversity or richness.

2 , and (2) positively correlated with species richness.

3 f the global variation in threatened species richness.

4 rse, including the highest mammalian species richness.

5 with the Cichlidae demonstrate lower species richness.

6 der increased as a function of their species richness.

7 large-scale patterns of diversification and richness.

8 itive relationship between host and parasite richness.

9 atively correlated with oceanic fish species richness.

10 ifferent extent depending on the anthocyanin richness.

11 e stress responses predict endophyte species richness.

12 n the relationship between host and parasite richness.

13 rank abundances along with little change in richness.

14 atial variation in global threatened species richness.

15 n compared to threshold responses in species richness.

16 tion of Bd infection intensity and bacterial richness.

17 imbuing the world with meaning, emotion, and richness.

18 ative profile but differed in their relative richness.

19 hos, and greatly diminished for fish species richness.

20 ns of biodiversity focus narrowly on species richness.

21 y the relationship between host and parasite richness.

22 xt half century despite increases in species richness.

23 osite pattern to global variation in species richness.

24 d maintains 73 +/- 12% of its unique species richness.

25 sity but higher bacterial and fungal species richness.

26 ected mean 1,400 y), to recover their former richness.

27 to the latitudinal gradient in tree species richness.

28 of species, but no net loss in local species richness.

29 ship between post-assembly host and parasite richness.

30 t tree species instead of increasing species richness.

31 Threatened, but not on overall bird species richness.

32 so enhance local fish abundances and species richness.

33 oplankton composition and abundance, but not richness.

34 es that influence global patterns of species richness(1-6).

35 mprise a greater proportion of local species richness (18-72% higher) and total abundance (21-144% hi

36 ted by significantly higher abundance (43%), richness (32%), PD (25%) and FD (25%) of birds visiting

37 having a greater stability abundance (18%), richness (38%), PD (32%), and FD (35%) of birds visiting

38 e analyse the most plausible pathways in the richness-abundance relationship and its stability along

39 rence was negatively related to native plant richness across all community types and ecoregions, alth

40 ersity) was composed of within-host parasite richness (alpha-diversity) and turnover (beta-diversity)

41 nificant differences in microbiome community richness, alpha-diversity, or structure between pediatri

42 explain the enormous differences in species richness among groups of organisms.

43 no consistent differences in relative tissue richness among studies.

44 owing the DWH, with a 38% decline in species richness and 26% decline in Shannon-Weiner diversity.

45 ad, they are caused by a decrease in species richness and abundance evenness, leading to declines in

46 Here, we relate trends in species richness and abundance from 21,500 terrestrial and marin

47 found a rapid increase in gut microbiome ARG richness and abundance in women from 2 independent ethni

48 However, we find increases in richness and abundance with increasing temperature and n

49 isation is driving rapid declines in species richness and abundance worldwide, but the general implic

50 is-derived microbiomes showed higher species richness and alpha diversity and clustered with their in

51 ing and foraging also decreased tree species richness and altered their composition.

52 ncreased in subjects with low bacterial gene richness and Bacteroides 2 enterotype, which have previo

53 Ectomycorrhizal fungal richness and beta-glucosidase activity were strongly red

54 Mean per-sampling event species richness and biomass were significantly higher in nutrie

55 New approaches go beyond traditional richness and co-occurrence studies to explicitly model b

56 plant encroachment influenced soil microbial richness and community composition across sites based on

57 s indicates that the observed spatiotemporal richness and community variability of AMF was largely in

58 richness and had various effects on species richness and composition of the insect groups.

59 t unique fractions of variation in microbial richness and composition.

60 connectivity and targeting regions with high richness and diverse landforms can mitigate these extinc

61 owing, and we observe increases in microbial richness and diversity as the host ages.

62 tion of SHI stood second in terms of species richness and diversity but resulted in low biomass and v

63 nchanged on the ski-runs over time but plant richness and diversity considerably increased, reaching

64 sults reveal that local trends of abundance, richness and diversity differ among biogeoregions, realm

65 Furthermore, fungal richness and diversity indices showed a positive correla

66 encing data can be used to assess the clonal richness and diversity of lymphocyte populations; to tra

67 The richness and diversity of such cutaneous bacterial commu

68 n, and elevation consistently correlate with richness and diversity of the skin microbiome and also p

69 on decreased sessile invertebrate abundance, richness and diversity on both natural and standardized

70 We also examined bee species richness and diversity with these two survey methods, an

71 In addition to richness and diversity, a dysbiosis index was calculated

72 ntrols were characterized by lower microbial richness and diversity, depletion of anaerobes, and shor

73 mycobiome, though crop management influenced richness and diversity, likely in response to difference

74 Unlike fungal richness and diversity, we observed compositional and fu

75 ic young are positively associated with host richness and diversity.

76 same reef can show very different microbial richness and diversity.

77 vertical stratification in bacterial species richness and evenness (alpha diversity) of the aerobiome

78 With the exception of species richness and exponential Shannon diversity, invasion inf

79 Development significantly increased species richness and exponential Shannon diversity, while invasi

80 periment, in which we aim to predict species richness and extinctions of arthropods immediately follo

81 t significant impact, and both plant species richness and floral abundance decreased with the additio

82 that communities with the greatest mutualist richness and functional redundancy are nearly two times

83 Theory suggests that high species richness and functional redundancy could promote mutuali

84 Digital health data capture the richness and granularity of individuals' behavior, the c

85 and sulphur-cycling); and (iv) that species richness and habitat stability are associated with high

86 hant disturbance increased butterfly species richness and had various effects on species richness and

87 protected areas can significantly impact the richness and identity of the species found there; one la

88 ted the association between predator species richness and incidence of rodent-borne haemorrhagic feve

89 s been associated with a decrease in species richness and increase in abundance of a few species that

90 thresholds in univariate metrics of species richness and indices of biotic integrity and has largely

91 d that lake stability is affected by species richness and lake size in both ecoregions and alkalinity

92 and found significant increase in taxonomic richness and larger representation of rare and clinicall

93 ing metrics) and ecological context (species richness and phylogenetic relatedness) in determining ch

94 between spatiotemporal variation in AMF OTU richness and plant species richness, root biomass, minim

95 nown about effects of within-species genetic richness and potential interactions between the two.

96 species added across experiments) on species richness and productivity.

97 fects on productivity via changes in species richness and soil pH over an experimental diversity grad

98 or disaster, human resilience depends on the richness and strength of social connections, as well as

99 ic factors influence the bacterial community richness and structure on the amphibian skin.

100 ycorrhizal species had higher soil bacterial richness and symbiont types had distinct soil microbial

101 n in saliva-serum showed the highest species richness and the highest similarity to the clinical inoc

102 under 80 species pools, varying species pool richness and the mean age of the sites from which the fu

103 ic network view, that causally links species richness and the other ecosystem components, is required

104 ver, there were only weak effects on species richness and the relative abundances of the octocoral sp

105 ment also has been shown to decrease species richness and to acidify soils, each of which may diminis

106 versity had dramatic impacts on the biomass, richness and traits of plant colonists.

107 ity influence geographic patterns of species richness and turnover.

108 However, regional variation in plant species richness and vegetation carbon stock can be substantial,

109 ccession based on the hypothesis that soil N richness and/or phosphorus (P) depletion become disadvan

110 h diversity partitioned between alpha (local richness) and beta (dissimilarity), and their change in

111 Overall, host richness predicted parasite richness, and as predicted, this effect was moderated by

112 tion to that, we found that their abundance, richness, and community structure also depend on geograp

113 fungal assemblages displayed high diversity, richness, and dominance indices, with the assemblage fou

114 significant compositional turnover, reduced richness, and evidence of negative MP influences.

115 explore what is known about parasite species richness, and identify some potential next steps towards

116 Fungal biomass, richness, and oxidative enzyme potential were reduced by

117 ncreases and decreases in abundance, species richness, and temporal species replacement (turnover) we

118 mice exhibited a reduction in fecal species richness, and that TCS further diminished microbial dive

119 s than would be expected given their species richness, and whether that is consistent across taxa, is

120 cts: heterozygosity (He = 0.667) and allelic richness (Ar = 4.298) were similar, and F(ST) was low (0

121 Host and parasite richness are generally positively correlated, but the st

122 onian fish community composition and species richness are influenced by water type, we conducted quan

123 hich find that native and non-native species richness are positively related at broad scales (small-s

124 we found that the areas having higher breed richness are undergoing land abandonment processes.

125 , many small patches generate higher species richness, are more likely to contain predators, and have

126 ughout the genome, telomeres, due to their G-richness, are particularly predisposed to forming these

127 ly being challenged by hypotheses that model richness as the overlap of species ranges, ultimately co

128 composition showed an increase in bacterial richness associated with altered microbiota composition.

129 We show that the effect of microbiota richness at 1 week on risk for AR at age 6 years was med

130 ctivity, soil fertility, and plant cover and richness at aridity values of 0.54, 0.7, and 0.8, respec

131 ere observed between the exposure to species richness at baseline and the onset of asthma and wheezin

132 Further, predation reduced invertebrate richness at both local and regional scales in the tropic

133 pogenic disturbance, we show that eukaryotic richness at the family level significantly increases wit

134 Despite no net change in species richness at the spatial scale of a study site, the losse

135 heterogeneity may cause a decline in species richness because it reduces the amount of effective area

136 tinct biotic composition and reduced species richness, biomass and soil organic matter.

137 Species richness, biomass, abundance, total bite rates and speci

138 ausal networks linking phytoplankton species richness, biomass, and physicochemical factors.

139 In addition, soil pH and plant community richness both explained significant variation in Strepto

140 roductivity generally increases with species richness, but less is known about effects of within-spec

141 o have been strong enough to deplete allelic richness by more than around 15%.

142 However, the increase in species richness by overcoming seed limitation did not lead to a

143 e ants instead responded to changes in plant richness by shifting their estimated trophic position.

144 The BEF theory states that higher species richness can enhance ecosystem functioning.

145 (1) EM fungal community composition, but not richness, changes along elevation, (2) there is no stron

146 This change in richness coincides with compositional changes, a decreas

147 le reduction in gene and metagenomic species richness compared with healthy subjects.

148 soil bacterial and fungal diversity (species richness, composition and beta-diversity) in a dry Medit

149 We examined fungal biomass, richness, composition and enzymes across three soil hori

150 he causes of continental patterns in species richness continue to spur heated discussion.

151 ps representing a gradient in plant resource richness (corn monocultures, fields dominated by native

152 This loss of richness correlated with disease stages and was particul

153 consistent findings that emotion vocabulary richness corresponds broadly with experience.

154 Endophyte richness decreased in plants with higher leaf nitrogen-t

155 forests and agricultural systems, functional richness decreases steeply and functional divergence mod

156 s Salween basin have markedly increased fish richness, density, and biomass relative to adjacent area

157 Decades of research suggest that species richness depends on spatial characteristics of habitat p

158 ype B was characterized by reduced microbial richness, depletion of Cutibacterium acnes, Dermacoccus

159 While species richness did not change, species composition and relativ

160 between primary and secondary forests in bee richness, diversity, evenness or abundance.

161 land use than widely used metrics of species richness, effective species numbers, and phylogenetic di

162 ferences between species can explain species richness effects, empirical evidence regarding functiona

163 led to date, to identify hotspots of species-richness, endemism and threatened species for the first

164 Rhizobacterial species richness enhanced per pot above- or below-ground dry mas

165 we show that, after controlling for species richness, environmental factors, such as temperature and

166 ies protective effects from predator species richness, epidemiological evidence is needed to bolster

167 five key dimensions of variation: perceptual richness, evaluative richness, integration at a time, in

168 rent aspects of functional diversity, namely richness, evenness, and divergence.

169 ajor dimensions of phytochemical diversity - richness, evenness, functional diversity, and alpha, gam

170 However, unlike species richness, evolutionary diversity does not continually in

171 esources, plant diversity [effective species richness, exp(H)], and community change (plant species t

172 ty at HLA-A, HLA-B and HLA-DRB1 and pathogen richness for a global dataset and for Native American po

173 resent more than 85% of the reported species richness for the country.

174 and for each plot estimated bird abundance, richness, functional diversity (FD) and phylogenetic div

175 , we estimated how much of regional parasite richness (gamma-diversity) was composed of within-host p

176 xperiment, we tested the impact of a species richness gradient (0, 1, 3, 5 or 6 species per community

177 gether generating a rare bimodal latitudinal richness gradient, and further analyses suggest that xer

178 Correspondingly, species but not genetic richness had a positive effect on stand-level tree bioma

179 adients, dissimilarity/overlap correlations, richness/harshness correlations, and nestedness of commu

180 High species richness has been documented in tropical agroforestry sy

181 has increased by ~ 60% and statewide species richness has increased by ~ 10% since 2001.

182 While taxonomic measures like species richness have been implemented, they do not fully grasp

183 Various taxonomic richness hotspots across the US represent focal regions

184 d strikingly accurate predictions of species richness immediately after the habitat loss disturbance,

185 nce from the local coast and possess limited richness in arid (< 5% moisture) and at high elevation s

186 st-understood network, and find a surprising richness in both a classical and quantum context.

187 ficant change in the microbial diversity and richness in dogs with congestive heart failure.

188 e of continental-scale processes for species richness in individual assemblages.

189 After controlling for higher baseline viral richness in mammals versus birds, the observed number of

190 ty dependence may even help maintain species richness in natural communities.

191 amount hypothesis predicts that (1) species richness in plots of fixed size (species density) is mor

192 r the relationship between host and parasite richness in response to global change, we experimentally

193 factorially manipulating species and genetic richness in subtropical China.

194 per species facilitated rather than reduced richness in the study communities.

195 : we find both greater reductions in species richness in the types of land use most disturbed by huma

196 roximations derived demonstrate a surprising richness including: independence of the firing rate to t

197 ate, such that in initially warmer locations richness increase is more pronounced while abundance dec

198 and the southern California Current species richness increased as did abundances of species associat

199 species of seed added, we found that species richness increased by about two species.

200 composed of weedy species, and even as their richness increased over decades to centuries, secondary

201 Fungal biomass and richness increased with simulated N deposition at sites

202 al Diversity Gradient (LDG), whereby species richness increases towards the Equator, results in highe

203 ltering post-assembly host species richness, richness-independent host phylogenetic diversity, and co

204 fference vegetation index (NDVI) and species richness index (SRI) were assessed at baseline to estima

205 f variation: perceptual richness, evaluative richness, integration at a time, integration across time

206 t be expected to occur where overall species richness is also high; however, this explains only a pro

207 Higher alien richness is observed in IUCN category-II national parks

208 tant within the tropics, where plant species richness is positively associated with the amount of rai

209 f the relationship between host and parasite richness is sensitive to parasite transmission, then cha

210 rdinarily diverse, but the estimated species richness is very much debated.

211 Increasing plant richness lengthened food chains by 10%-20% compared to m

212 munities if not for nitrogen-induced species richness losses.

213 creasing network size also increases species richness monotonically, producing characteristic species

214 e changes in the marine realm, where species richness mostly increases with warming.

215 suggest that older regions have higher local richness not simply because older pools are more specios

216 , composed of the interactions among species richness, nutrient cycling, and phytoplankton biomass, w

217 tworks from correlations between the species richness of 16 trophic groups, 10 ecosystem functions, a

218 day of antibiotics was associated with lower richness of anaerobes and butyrate-producers within 1 we

219 rished signals may not fully account for the richness of auditory information provided by visual spee

220 ic fever with renal syndrome and the species richness of both avian and mammalian predators; the tren

221 sessment that can take advantage of the full richness of data described in natural language in primar

222 ies are likely to provide the resolution and richness of data required to generate such clinically re

223 ating ants + spiders); abundance and species richness of Diptera, pollinator insects, spiders, and pr

224 cities from the estimated game, we find the richness of education resources is the most critical det

225 is known about the relationship between the richness of hippocampal vascular supply and cognition.

226 roversy lies the question of whether species richness of individual grid cells is controlled by local

227 st needs to be left unlogged to maintain 90% richness of its unique species, whereas retaining 50% of

228 We experimentally manipulated the species richness of marine phytoplankton communities under a ran

229 anations for the equator-to-poles decline in richness of most groups of organisms, namely the latitud

230 the links between livestock diversity -i.e. richness of native breeds- and a selection of environmen

231 day of antibiotics was associated with lower richness of obligate anaerobes (adjusted risk ratio [aRR

232 tibiotic type and duration of therapy on the richness of obligate anaerobes and known butyrate-produc

233 This suggests that the apparent richness of perception across saccades may be supported

234 The abundance, diversity and species richness of phytophagous Coleoptera and total predators

235 assess the abundance, diversity and species richness of phytophagous, pollinators and predators arth

236 5% of threatened and ~30% of endemic species richness of primary Atlantic forest.

237 es at further spatial distances, and species richness of street trees at any distance, were not assoc

238 Unexpectedly, the OTU richness of the communities after 21 weeks was indisting

239 The richness of the framework presented in this study reinfo

240 Prolonged ART may restore the richness of the microbiota closer to that of HIV-uninfec

241 The extraordinary variability and richness of their structures afford engineering synergie

242 Plant species richness (of all living stems >10 cm in diameter) ranged

243 so, we measure the effects of basal resource richness on food chain length, niche breadth and trophic

244 early-life exposure to greenness and species richness on the development of allergic diseases and ast

245 We show that positive effect of species richness on tree abundance only prevails in eight of the

246 do not detect systematic temperature-related richness or abundance trends on land, despite a greater

247 gh the relative abundance of bacteria, their richness or diversity did not significantly differ betwe

248 Principles from linguistics suggest that the richness or diversity of individuals' actively used emot

249 t individual quantities (e.g., total species richness or nutrients) were not significant predictors o

250 lights possible temporal declines in species richness over 30 years and thus the need for future inte

251 ife microbial diversity was lower at 1 week (richness P = .0079) in children with AR at age 6 years,

252 vely associated with bacterial diversity and richness (P < .05).

253 The abundance (p = 0.006) and richness (p = 0.013) of the eukaryotic virome increased

254 2.78log(10) vs. 0.83log(10), p = 0.002), and richness (p = 0.016) were inversely associated with poli

255 These differences include lower community richness (p(adj) = 0.01) in the settled dust of moldy ho

256 th many animals, large animals, high species richness (particularly of mammals), and which are dissim

257 te counting procedure to determine endophyte richness patterns among plant tissue types.

258 hange and why they often have shared species richness patterns, biogeographic regions, biomes and bio

259 s of species diversification, which underlie richness patterns.

260 In contrast, mariculture species richness potential is projected to increase by about 40%

261 ecline of 1.3% and 5% in mariculture species richness potential under RCP 2.6 ('strong mitigation') a

262 d that root composition and biomass, but not richness, predict unique fractions of variation in micro

263 Overall, host richness predicted parasite richness, and as predicted,

264 nt a severe decline in high latitude species richness presaged by ecologic reorganization during the

265 erived carbon inputs at higher plant species richness (PSR).

266 main of how global change impacts on species richness, relative abundance and species composition.

267 ssembly, altering post-assembly host species richness, richness-independent host phylogenetic diversi

268 iation in AMF OTU richness and plant species richness, root biomass, minimal changes in soil texture

269 igm is grounded in first principles: species richness scales with area, and surface area and niche de

270 ypothesis using 24 456 observations of plant richness spanning four community types and seven ecoregi

271 mean annual temperature and plant community richness (Spearman's r: 0.77, 0.64 and -0.79, respective

272 Within the human-modified landscape, species richness, species abundance and community composition re

273 In arthropod community ecology, species richness studies tend to be prioritised over those inves

274 f generalist ants did not vary with resource richness, suggesting they were limited by optimal diet r

275 ysis revealed that bee abundance and species richness tended to increase in response to fire, differi

276 Global analyses reveal hotspots of species richness, together generating a rare bimodal latitudinal

277 show how coral biodiversity metrics (species richness, total abundance and probability of interspecif

278 s likely due to different macrophyte species richness, underlying hard substrate in natural macroalga

279 del predictors explained part of the species richness variability but not relative abundance nor spec

280 more, trait responses to species and genetic richness varied significantly within and between species

281 While plant species richness was controlled by climate and soil water availa

282 een the size, number of patches, and species richness was greatly affected by insufficient monitoring

283 In larval stages, bacterial OTU richness was highest in samples exposed to malathion, in

284 Total species richness was highest in the southern portion of CT, like

285 f beetles and ants collected although beetle richness was significantly higher in burned logs two wee

286 Bacterial richness was significantly higher in larval stages compa

287 While insect species richness was unaffected by fertiliser treatment, fertili

288 , our results show that while insect species richness was unaffected by fertilisers, network structur

289 een ecological differentiation and taxonomic richness was weak early in the evolution of animals but

290 averaging several methods to estimate total richness, we confirm that over 15,000 tree species are e

291 the exception of districts with low species richness, we found a significant negative association be

292 ecological communities such as abundance and richness, we know relatively little about nutritional ge

293 lant influence, as soil fungal and bacterial richness were either higher or lower in woody encroached

294 n-fixing woody plants had higher soil fungal richness, while Ecto/Ericoid mycorrhizal species had hig

295 , we hypothesize that rhizobacterial species richness will alter sorghum (Sorghum bicolor L.) growth,

296 sociation of street tree density and species richness with antidepressant prescribing for 9751 inhabi

297 We then assess gamma-diversity (regional richness) with diversity partitioned between alpha (loca

298 uired to obtain accurate measures of species richness within a region.

299 e recovery of threatened and endemic species richness, within isolated secondary forest (SF) fragment

300 esponse ratio applied to measures of species richness yielded better accuracy than the commonly used