ライフサイエンスコーパス: meadow

1 on environmental context in a Tibetan alpine meadow.

2 s, and were either sheep pasture or ungrazed meadow.

3 ively unknown, particularly in Xizang alpine meadow.

4 e Bahama Banks, the world's largest seagrass meadow.

5 ts on root decomposition in a Tibetan alpine meadow.

6 r visitors in a diverse Mediterranean flower meadow.

7 ments colonized by eelgrass (Zostera noltei) meadows.

8 than mixed and conifer dominated stands and meadows.

9 ides were prevalent in undisturbed wet sedge meadows.

10 patterns and rings in Mediterranean seagrass meadows.

11 angrove forests, tidal marshes, and seagrass meadows.

12 ects in the spatial self-organization of the meadows.

13 nthropogenic influence on Maldivian seagrass meadows.

14 emissions following disturbance of seagrass meadows.

15 ajor part of plant biomass in Tibetan alpine meadows.

16 ls at paired sites without adjacent seagrass meadows.

17 tant for conservation management of seagrass meadows.

18 sive shallow-water banks covered in seagrass meadows [2], where fishermen deploy artificial shelters

19 in large numbers in the high-altitude Alpine meadow [6, 7].

20 restoration trajectories: an equilibrium in meadows, a non-linear increase across steppes, and an ab

21 lable and provide a complete distribution of meadows across the basin.

22 ples from three Tibetan ecosystems-an alpine meadow (AM), alpine steppe (AS), and desert steppe (DS)-

23 The estimated regression of meadows amounted to 34% in the last 50 years, showing th

24 n area was 2.5 and 4 times lower than in the meadow and forest areas, respectively.

25 n of the treeline would be at the expense of meadow and shrub species and radically change this high-

26 hment by transplanting soil and seedlings of meadow and tree species across climate gradients on Moun

27 ution of P. oceanica, (ii) the total area of meadows and (iii) the magnitude of regressive phenomena

28 (III) oxyhydroxides in undisturbed wet sedge meadows and calcium (Ca) in disturbed pond sediments.

29 Meadows and crop diversity, respectively, supported inse

30 01 individuals with extinction data from 279 meadows and mortality of 1,742 larval nests in a butterf

31 fritillary butterfly occupying a set of dry meadows and pastures in the angstromland islands - to in

32 ity of alpine grasslands, composed of alpine meadows and steppes, in the Tibetan Plateau has an essen

33 w of Phytomyxea as rare entities in seagrass meadows and suggest their generally low pathogenicity in

34 , while the afforestation of arable land and meadows and the overgrowth of bare mudflats with willow

35 IT being marginally better for beetles from meadows and the SD better for beetles from OSR fields.

36 the most likely migration corridors between meadows and used the unique cubist machine learning appr

37 botanical origin (acacia, sunflower, linden, meadow, and fake honey) by recording emission from 270 t

38 e fractional land cover of cultivated crops, meadow, and herbs indicating land disturbance as potenti

39 sm that enhances connectivity among seagrass meadows, and aids in resilience and recovery of these co

40 ased estimates of mangrove forests, seagrass meadows, and macroalgal habitats in 69 study areas spann

41 odiversity held in its coral reefs, seagrass meadows, and mangrove forests, all of which are in globa

42 ylands, peatlands, salt marshes, or seagrass meadows, and the mechanisms behind this phenomenon are s

43 tive growth coalesces plants into continuous meadows, and this Allee effect has slowed the rate of sp

44 Seagrass meadows are an important and threatened ecosystem.

45 Seagrass meadows are considered important natural carbon sinks du

46 Posidonia oceanica meadows are declining at alarming rates due to climate c

47 Seagrass meadows are important sites for carbon storage.

48 nificant shifts for management: Widgeongrass meadows are not only responsible for rapid, extensive re

49 osomal RNA gene, we found that when seagrass meadows are present, there was a 50% reduction in the re

50 Seagrass meadows are the most widespread coastal ecosystem on the

51 Seagrass meadows are threatened by multiple pressures, jeopardizi

52 Alpine meadow areas experienced strong increases in carbon sequ

53 ic) was 0.5 times higher than the forest and meadow areas.

54 y foraged on the same North African seagrass meadows as their modern-day counterparts.

55 ed that the crane prefers to breed in alpine meadows at an elevation over 2,800 m, a maximum temperat

56 clining to 1.06 mg C(org) cm(-3) in seagrass meadows at the estuary mouth, despite a general gradient

57 bivores undergo range expansion, turtlegrass meadows at their northern limit display reduced resilien

58 tle abundance will increase, leading to more meadows being returned to their natural grazed state.

59 Goldin-Meadow & Brentari (G-M&B) are implicitly going against t

60 Goldin-Meadow & Brentari (G-M&B) argue that, for sign language

61 In their article, Goldin-Meadow & Brentari (G-M&B) assert that researchers must d

62 Goldin-Meadow & Brentari (G-M&B) challenge the traditional sepa

63 In their target article, Goldin-Meadow & Brentari (G-M&B) discuss several observations s

64 gn language iconicity suggests, as do Goldin-Meadow & Brentari (G-M&B) in their target article, that

65 al research in cognition presented by Goldin-Meadow & Brentari (G-M&B) indicates a more complex pictu

66 Goldin-Meadow & Brentari (G-M&B) outline several criteria for d

67 Goldin-Meadow & Brentari (G-M&B) rely on a formalist approach t

68 idence for the viewpoint advocated by Goldin-Meadow & Brentari (G-M&B) that sign, speech, and gesture

69 We applaud Goldin-Meadow & Brentari's (G-M&B's) significant efforts to con

70 ology and work by Ford and colleagues on the meadow brown butterfly Maniola jurtina did much to ignit

71 y, ants increased aphid population growth in meadow but not understory environments.

72 ortical (pCorA) and medial (pMeA) nuclei, in meadow, but not prairie, voles.

73 ming favors the NDVI enhancement of degraded meadows, but higher temperatures limited the restoration

74 The sedimentary C(org) underneath seagrass meadows came principally from allochthonous (non-seagras

75 that C(org) stored in sediments of seagrass meadows can be highly variable within an estuary, attrib

76 r 24 Asteraceae species growing in an alpine meadow community (Sichuan Province, China).

77 oil, and vegetation features most facilitate meadow connectivity?

78 Lieber-DeCarli diet (LD) and Meadows-Cook diet (MC) are the most accepted models of c

79 Meadow degradation also increased AM fungal biomass allo

80 stematic understanding of these responses to meadow degradation remains relatively unknown, particula

81 gi increased with the increasing severity of meadow degradation, indicating greater dependence of hos

82 ill provide a basis for identifying areas of meadow degradation, or stability and recovery, and poten

83 Meadows dominated by seagrasses with persistent life-his

84 ly Quaternary Period (2.73-1.54 Ma) and to a meadow-dominated ecosystem after ~1.54 Ma, along with gl

85 but more precipitation might be useless for meadows due to lower temperatures and for desert-steppes

86 top chambers to induce warming in an alpine meadow ecosystem from 2012 to 2014.

87 Tibetan Plateau supports the largest alpine meadow ecosystem globally.

88 nd herbivore trophic levels in a New England meadow ecosystem.

89 ay help to facilitate the adaption of alpine meadow ecosystems to changing climate.

90 e grazing effects on carbon fluxes in alpine meadow ecosystems, we used a paired eddy-covariance (EC)

91 adients into subalpine/alpine meadows, while meadows expand upward onto bare ground.

92 Conversely, seagrass meadow extent was more likely to be increasing when thes

93 Rapidly declining trajectories of seagrass meadow extent were most strongly associated with high pr

94 Resistance was found in the meadow fescue (Festuca pratensis) to crown rust (Puccini

95 This is also the case in meadow fescue (Festuca pratensis), which is known for go

96 m), perennial rye-grass (Lolium perenne) and meadow fescue (Festuca pratensis).

97 iegelii are fungal symbionts (endophytes) of meadow fescue (MF; Lolium pratense), which they protect

98 obust cytogenetic markers for karyotyping of meadow fescue and ryegrass species and their hybrids.

99 ted and more stress-resistant grass species, meadow fescue Festuca pratensis.

100 new approach to analyze the large genome of meadow fescue, which involves the reduction of sample co

101 astrophic losses of habitat-forming seagrass meadows followed [2], along with mass mortalities of inv

102 They form extensive meadows found globally that bioengineer their local envi

103 We resampled eelgrass (Zostera marina) meadows from published studies to determine variability

104 s largest freshwater wetland, the Grand Lake Meadows (GLM) and the associated Saint John/Wolastoq Riv

105 stigations in a wet meadow (WM), a grassland meadow (GM), a moderately degraded meadow (MDM) and a se

106 in a Caribbean Thalassia testudinum seagrass meadow, grazed areas maintained net positive metabolic c

107 Instead, open meadows had higher ant abundance and per capita rates of

108 mount of four types of seminatural habitats (meadows, hay, forests, and hedgerows) in the landscape o

109 the possibility to distinguish sunflower and meadow honey samples regarding examined physicochemical

110 ply the model to a case study for a seagrass meadow in Australia.

111 iance data from a snow-scoured alpine tundra meadow in Colorado, USA, where solifluction lobes are as

112 rass biomass in a large approximately 250 ha meadow in tropical north east Australia.

113 ers in the 7-km(2) Zostera marina (eelgrass) meadow in Virginia, U.S.A., part of the largest, most co

114 was significantly higher in aspen stands and meadows in early summer but converged to similar levels

115 et they form densely vegetated, multispecies meadows in oligotrophic tropical waters.

116 plantings in the Central Valley and montane meadows in the Sierra.

117 ary, from 52.16 mg C(org) cm(-3) in seagrass meadows in the upper parts, declining to 1.06 mg C(org)

118 sing sediment cores from 86 sites (across 21 meadows) in Back Sound, North Carolina, USA.

119 ific Advisory Board of the following: Modern Meadow, Inc., Recombinetics, Inc., and Sample6, Inc.'.

120 r infaunal prey in eelgrass (Zostera marina) meadows increases genetic diversity by promoting conditi

121 e gas emissions, the current Tibetan Plateau meadow is at risk of major transformation.

122 Long-term "Blue Carbon" burial in seagrass meadows is complicated by other carbon and alkalinity ex

123 m based on poliphytic forages from permanent meadows is enhancing milk's nutritional quality due to a

124 The areal extent of seagrass meadows is in rapid global decline, yet they provide hig

125 (-1)), NEP in grazed Caribbean T. testudinum meadows is similar to that in many other ungrazed system

126 ody temperature, and respiratory rate of the meadow jumping mouse during hibernation cycles.

127 Seagrass meadows, key ecosystems supporting fisheries, carbon seq

128 The UNESCO World Heritage site of L'Anse aux Meadows (LAM) in northern Newfoundland is the only undis

129 We estimate that shallow seagrass meadows (<5 m depth) had significantly higher C(org) sto

130 e polygynous montane (Microtus montanus) and meadow (M. pennsylvanicus) voles and the monogamous pine

131 lt female prairie (Microtus ochrogaster) and meadow (M. pennsylvanicus) voles were compared to examin

132 t carbon sequestration potential of seagrass meadows may be overestimated if calcification-induced CO

133 grassland meadow (GM), a moderately degraded meadow (MDM) and a severely degraded meadow (SDM) from A

134 acacia, and about 20% for both sunflower and meadow mix.

135 sing CH(4) 8-fold to 0.8 g m(-2) yr(-1), the meadow now offsets 0.42 tCO(2)e ha(-1) yr(-1), which is

136 we investigated methane turnover in seagrass meadows of Posidonia oceanica in the Mediterranean Sea.

137 Here, we use the iconic seagrass meadows of Shark Bay, Western Australia--a relatively pr

138 uxes in adjacent fenced (FM) and grazed (GM) meadows on the Tibetan plateau.

139 n regions (grassland deriving from permanent meadows) on the chemical fingerprint of Parmigiano Reggi

140 nd a treeline instead of the existing alpine meadow or Arctic tundra.

141 pes, but did not do so efficiently on either meadows or desert-steppes.

142 idal Enhalus acoroides (L.f.) Royle seagrass meadow over eleven years revealed a declining trend in a

143 c diversity and structure within and between meadows over 5-12 years.

144 ural grasslands (in a broad sense, including meadows, pastures, lowland and upland heathlands and ope

145 o be more than 17-fold more abundant on open meadow plants than on shaded understory plants.

146 alescent low center polygon, polygon trough, meadow, ponds, rivers, and lakes, to determine their spa

147 ution of ALAN to the global loss of seagrass meadows, posing questions about key interactions with a

148 y across elevation, with bare soil above the meadows potentially poorer for plant establishment.

149 tential applicability in an array of diverse meadows primarily focusing on drug delivery, biosensing

150 binger of the terminal state of the seagrass meadows prior to their collapse.

151 a self-thinning response, increases LAI and meadow production in shallow depths.

152 Additionally, grazing did not change the meadow production to respiration ratio, indicating it di

153 Seagrass meadows provide important ecosystem services and are cri

154 Seagrass meadows provide numerous ecosystem services and their ra

155 Ecological restoration of forests, meadows, reefs, or other foundational ecosystems during

156 rtant threshold for the forest expansion and meadow resilience loss on the Tibetan Plateau.

157 A., part of the largest, most cost-effective meadow restoration to date, to provide the first seagras

158 rimental impact on seagrass, fragmenting the meadows, resulting in the habitat degradation.

159 Dioecious members of the genus Thalictrum (meadow-rue), however, produce flowers that lack aborted

160 The meadows sampled (San Francisco, Tomales and Bodega Bays

161 egraded meadow (MDM) and a severely degraded meadow (SDM) from April to October 2011.

162 building corals located adjacent to seagrass meadows showed twofold reductions in disease levels comp

163 each with and without symbionts, in five wet meadow sites to expose them to a natural assembly of ene

164 an those of depth, temperature, latitude, or meadow size.

165 xpansion at meadows' upper edges, while rich meadow soil might facilitate contraction at lower edges

166 ppearance, with somewhat smaller declines in meadow soil.

167 snow disappearance, with larger increases in meadow soil.

168 soil composition, and proportion of till and meadow soils in the catchment.

169 with contrasting land management (forest and meadow soils), which have been affected by emissions fro

170 mite toad (Anaxyrus canorus) is a species of meadow-specializing amphibian endemic to the high-elevat

171 The method uses the xylem-feeding insect the meadow spittlebug (Philaenus spumarius L. [Homoptera: Ce

172 n the genetic basis of colour pattern in the meadow spittlebug P. spumarius.

173 The meadow spittlebug, Philaenus spumarius (L.) (Hemiptera,

174 Using the meadow steppe (grassland) study site of Inner Mongolia,

175 zing is the primary land use in the Hulunber meadow steppe.

176 Seagrass meadows store globally significant organic carbon (C(org

177 ated oilseed rape (OSR) fields and unsprayed meadows, subjected to repeated insecticide treatments.

178 networks were more complex in more degraded meadows, supporting the stress gradient hypothesis.

179 re influences ecosystem carbon dynamics in a meadow system.

180 abundant and apparent in most grassland and meadow systems, as they were in the present experiments.

181 ce of a global long-term decline in seagrass meadows that is widely attributed to anthropogenic activ

182 igher in aspen stands than conifer stands or meadows throughout the summer.

183 demonstrates the susceptibility of seagrass meadows to damage from swing moorings.

184 be a progressive transition from homogeneous meadows to extinction through dynamical regimes that all

185 changing environments that ranged from fern meadows to woodland mosaics, naturally burned landscapes

186 inator species from study plots in subalpine meadows, to test the hypothesis that interactions betwee

187 By contrast, low-latitude meadows tolerated herbivory due to high insolation which

188 community by transplanting replicated alpine meadow turfs downslope along an elevational gradient the

189 e to a standard swing mooring, in a seagrass meadow under high tidal influence.

190 r-water CO(2) exchange in a typical seagrass meadow underlain by carbonate sediments.

191 Poor soil might constrain expansion at meadows' upper edges, while rich meadow soil might facil

192 vole, and two promiscuous vole species, the meadow vole and montane vole.

193 erence formation in the socially promiscuous meadow vole by using viral vector V1aR gene transfer int

194 could contribute to seasonal differences in meadow vole social behavior.

195 prairie vole, but not in the non-monogamous meadow vole.

196 In Experiment 1, individually housed male meadow voles (Microtus pennsylvanicus) and prairie voles

197 structure in nature, whereas closely related meadow voles (Microtus pennsylvanicus) are solitary and

198 Female meadow voles (Microtus pennsylvanicus) are territorial d

199 Nonmonogamous meadow voles (Microtus pennsylvanicus), which exhibit se

200 ramble competition, respectively, among male meadow voles (Microtus pennsylvanicus).

201 and parentally inexperienced or experienced meadow voles (Microtus pennsylvanicus).

202 voles (Microtus ochrogaster) and promiscuous meadow voles (Microtus pennsylvanicus).

203 ERalpha-IR in the MeA than male montane and meadow voles and in the BST relative to montane males.

204 Meadow voles are seasonally social rodents that form non

205 ference was not facilitated in nonmonogamous meadow voles by introducing oxytocin receptor into the n

206 Data support the hypothesis that captive meadow voles develop selective and enduring same-sex soc

207 Male and female meadow voles differed in the ventromedial hypothalamus,

208 LPS-injected male prairie and meadow voles engaged in less social contact with female

209 Meadow voles exhibited social preferences but low social

210 Meadow voles had a higher density of cells labeled with

211 Meadow voles had more ERalpha-labeled cells in the pCorA

212 Female prairie and meadow voles worked harder to access familiar versus unf

213 gamous prairie voles) or peers (group-living meadow voles).

214 ted monogamous prairie voles and promiscuous meadow voles, and compare receptor densities across sexe

215 d in the BST of male and female hamsters and meadow voles, but not in rats.

216 e cells in male and female hamsters and male meadow voles, but not rats.

217 Prairie voles have more Oxtr+ cells than meadow voles, but Oxtr distribution across dopamine-rece

218 ltiple brain regions in short day lengths in meadow voles, but we found no concomitant change in PVN

219 ns were highly conserved between prairie and meadow voles, including many subnuclei examined within t

220 Here we show that male meadow voles, Microtus pennsylvanicus, increase their sp

221 Female prairie voles, but not meadow voles, spent more time in the chamber with saline

222 n found between prairie voles and polygamous meadow voles.

223 r density and social behavior in prairie and meadow voles.

224 airie voles compared to congener promiscuous meadow voles.

225 ternative reproductive phenotypes among male meadow voles.

226 n sexually naive and mate-paired prairie and meadow voles.

227 We explored how light environment (open meadow vs. shaded understory) mediates the abundance and

228 au, with the exception that OCD in the swamp meadow was substantially higher than that in surrounding

229 is showed that the mortality of beetles from meadows was much higher after the first treatment than a

230 stewater samples were collected from Truckee Meadows Water Reclamation Facility (TMWRF) from November

231 In the dung-decomposer food web of an alpine meadow, we predicted that in the presence of above-groun

232 phages isolated from Mediterranean seagrass meadows, we found that the type III-B machinery co-opts

233 t established in recently disturbed seagrass meadows, we used previous estimates of risk-sensitive du

234 While alpine meadows were relatively strong carbon sinks, the semiari

235 l (acacia and sunflower) and one polyfloral (meadow) were collected from the Autonomous Province of V

236 A nearby meadow wetland accumulated over 300 times more carbon (N

237 The meadow wetland appeared more suitable to assess plant pr

238 hange (NEE) of CO2 with polar semidesert and meadow wetland landscapes at the highest latitude locati

239 lar semidesert landscape, and was similar to meadow wetland NEE at much more southerly latitudes.

240 At the meadow wetland, soil heating enhanced plant growth, whic

241 We apply this model to Posidonia oceanica meadows, where positive and negative feedbacks are well

242 dominated, mixed, conifer dominated or open meadow, which includes the range of vegetation condition

243 lands, mangroves, salt marshes, and seagrass meadows, which greatly exceed those of oceanic and fores

244 This includes seagrass meadows, which have received relatively little attention

245 long climate gradients into subalpine/alpine meadows, while meadows expand upward onto bare ground.

246 some of the impacts of moorings on seagrass meadows, whilst accommodating for tidal fluctuations.

247 uncertainty around whether Bahamian seagrass meadows will remain a net carbon sink.

248 of summation operator26PFASs, while a simple meadow with ground elder can remove 0.55 g yr(-1) ha(-1)

249 We conducted investigations in a wet meadow (WM), a grassland meadow (GM), a moderately degra

250 tributing to the ongoing decline of seagrass meadows worldwide; yet the diversity and ecology of the

251 from apiaries of the agricultural, hills and meadow zones of the south east region of Buenos Aires pr