ライフサイエンスコーパス: meadow

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

2 r visitors in a diverse Mediterranean flower meadow.

3 on environmental context in a Tibetan alpine meadow.

4 ls at paired sites without adjacent seagrass meadows.

5 tant for conservation management of seagrass meadows.

6 ments colonized by eelgrass (Zostera noltei) meadows.

7 than mixed and conifer dominated stands and meadows.

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

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

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

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

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

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

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

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

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

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

18 Seagrass meadows are an important and threatened ecosystem.

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

20 Seagrass meadows are important sites for carbon storage.

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

22 Seagrass meadows are the most widespread coastal ecosystem on the

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

73 Seagrass meadows provide numerous ecosystem services and their ra

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

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

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

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

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

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

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

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

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

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

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

85 re influences ecosystem carbon dynamics in a meadow system.

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

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

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

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

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

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

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

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

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

95 Female meadow voles (Microtus pennsylvanicus) are territorial d

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

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

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

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

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

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

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

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

104 Meadow voles had a higher density of cells labeled with

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

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

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

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

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

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

111 airie voles compared to congener promiscuous meadow voles.

112 ternative reproductive phenotypes among male meadow voles.

113 n found between prairie voles and polygamous meadow voles.

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

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

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

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

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

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

120 The meadow wetland appeared more suitable to assess plant pr

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

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

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

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

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

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

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

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