ライフサイエンスコーパス: pasture

1 by oral consumption of contaminated food or pasture.

2 ates of land use change, primarily to cattle pasture.

3 ths was similar in all fragments and even in pasture.

4 (N = 7) were kept in a temperate habitat on pasture.

5 yunsaturated FAs which were prevalent in the pasture.

6 er density, and isolated individual trees in pasture.

7 and a subsidy for cattle from semi-intensive pasture.

8 rigated shrub/grasslands and irrigated crops/pastures.

9 ents such as soils of temperate woodland and pastures.

10 cloud forest landscapes threatened by cattle pastures.

11 2 emission processes, particularly in grazed pastures.

12 agricultural production of legume crops and pastures.

13 rom native forest to deforested cropland and pasture?

14 (intact woodland=12.6 trees ha(-1); isolated pasture=1.7 trees ha(-1); population area=10 km(2)).

15 itation gradient and C gains were greater as pastures aged.

16 alfalfa, and N yield by corn, soybeans, and pasture, although their relative importance varied among

17 nventional drained agricultural peatlands (a pasture and a corn field) and three flooded land-use typ

18 policies: a tax on cattle from conventional pasture and a subsidy for cattle from semi-intensive pas

19 Intercropping with pasture and detoxifying seedcake yield coproducts that a

20 Proportion of pasture and forest patch density structured the frugivor

21 l and per country due to global agriculture, pasture and forestry by combining high-resolution land u

22 spectroscopy methods to distinguish between pasture and preserved-forage cheeses.

23 wed by C (GSC), or GS followed by 100days at pasture and then C (GSPC), and slaughtered at 3 target c

24 of the Amazonian forest has been cleared for pastures and agriculture, one fourth of the remaining fo

25 d adipose fat from animals raised on similar pastures and fodders have distinct isotopic signatures.

26 resulting from using fire to clearing dense pastures and forests for reclaiming.

27 ave been in developing countries, displacing pastures and resulting in an estimated 2 million hectare

28 ased following afforestation on cropland and pasture, and in tropical, subtropical and boreal zones.

29 ical countries, where more manure is left on pastures, and dung beetles remove and aerate dung faster

30 is explored for both clean and contaminated pastures, and the impact of faecal avoidance behaviour a

31 Major terpenoids and tocols in the pasture appeared as major ones in milk and cheese, where

32 night when ambient conditions in forest and pasture are most similar; butterflies face substantial d

33 o cropland expansion into previously cleared pasture areas (74%) or forests (26%).

34 mportant source of uncertainty in forest and pasture areas originates from different input data appli

35 vasive species, climate change, cropland and pasture areas; additionally, a significant proportion of

36 tioxidant and fatty acid (FA) composition of pasture as well as those of milk and cheese from a comme

37 gnificantly lower digestive quality than the pasture average.

38 Pasture-based livestock systems are often associated wit

39 The PASTURE birth cohort followed 983 infants from rural are

40 Against Allergy Study in Rural Environments (PASTURE) birth cohort (cord blood [n = 836], 1 year [n =

41 against Allergy-Study in Rural Environments (PASTURE) birth cohort including 793 children from rural

42 gainst Allergy: Study in Rural Environments (PASTURE) birth cohort study, 1133 pregnant women were re

43 gainst allergy: Study in Rural Environments (PASTURE) birth cohorts and compared with classical nondi

44 rease PAs in forage legumes for reduction of pasture bloat in ruminant animals.

45 is an important agronomic trait, preventing pasture bloat in ruminant animals.

46 om the conversion from forest (C3 plants) to pasture (C4 plants) by analysing total SOC stocks and th

47 ages such as harvesting of medicinal plants, pasturing cattle and forest fires can induce environment

48 physiologically based demographic models of pasture, cattle, and pastoralists and a bioeconomic mode

49 Cytokine levels were measured in the PASTURE cohort.

50 gainst Allergy: STUdy in Rural Environments (PASTURE) cohort.

51 renne), (b) a medium digestibility permanent pasture comprising a range of grass species, and (c) a r

52 elatively low digestibility native grassland pasture comprising mainly Molinia caerulea.

53 E installations are located in croplands and pastures, comprising 155 km(2) of change.

54 newly converted cropland (from forestry and pasture) contributing most of the variance in estimated

55 C (SOC) dynamics along 20 years of forest-to-pasture conversion in two subregions with different mana

56 However, 20 years after forest-to-pasture conversion SOC in HG decreased by 20%, whereas i

57 Milk from cows at pasture could easily be distinguished from milk from sta

58 een produced by sequentially fewer adults in pasture, creating a genetic bottleneck.

59 effects of pearl millet (PM) vs. cool-season pasture (CSP) on animal performance and milk FA in a gra

60 cessful but then declined by 44% (leading to pasture damage of c. 160 million New Zealand dollars per

61 nt class analysis model with the best fit to PASTURE data separated 4 phenotypes of atopic dermatitis

62 GHG emissions at three scales: the dung pat, pasture ecosystem, and whole lifecycle of milk or beef p

63 (56 farm and 55 reference children) from the PASTURE/EFRAIM birth cohort (flow cytometry).

64 s with different management practices during pasture establishment in the Colombian Amazon: high-graz

65 Pasture establishment increased SOC contents across all

66 h subregions and soil N stock changes during pasture establishment were correlated with SOC changes.

67 s and the natural abundance of (15) N during pasture establishment.

68 Pasture exhibited higher C: N ratios than cropland in th

69 deforestation between the two periods, with pasture expansion accounting for most remaining deforest

70 d fuel is now a major driver of cropland and pasture expansion across much of the developing world.

71 tion, different milk varieties obtained from pasture-fed animals were analysed, providing, for the fi

72 not exclusive to either farming system, and pasture feeding conventional cows will remove difference

73 an environmental mixture of ECs derived from pastures fertilized with sewage sludge (biosolids): a co

74 sion due to an influx of swans from adjacent pasture fields.

75 rall, C inputs (including C input amount and pasture frequency in the crop rotation system) accounted

76 less than in adjacent plots of a less-common pasture grass (Lolium multiflorum), indicating that resi

77 (7 yr at the time of sampling) in which a C4 pasture grass (Paspalum notatum) was grown on a sandy lo

78 ts (endophytes) living on certain species of pasture grasses and protect the host plant from insect h

79 s grown in an intercropping arrangement with pasture grasses so that Jatropha is coproduced with catt

80 ajor herbicides); (2) Lolium spp., important pasture grasses, yet herbicide-resistant weeds in crops;

81 present in meaningful amounts in the milk of pasture-grazed cows, might offset the adverse effect of

82 or cow milk in terms of fresh grass feeding, pasture grazing and organic/biodynamic farming.

83 All farms applied year-round pasture grazing.

84 Pasture-grazing dairy cows have more CLA in their milk t

85 n Costa Rica-a country that uses traditional pasture-grazing for dairy cows.

86 g the removal of S. invicta from a disturbed pasture habitat, but moderate loss of diversity associat

87 pecies in soil clay fractions from an upland pasture hillslope.

88 For Europe, the controversial wood-pasture hypothesis posits that grazing by wild large her

89 6-y-old plantations established in abandoned pasture in lowland Costa Rica, we used a mass-balance ap

90 an enclosed area of Ixodes ricinus-infested pasture in North Wales, United Kingdom, and rapidly acqu

91 nails were collected from stream waters on a pasture in Siskiyou County, Calif., where PHF is enzooti

92 sions after land-cover change from forest to pasture in the Colombian Amazon.

93 uliginosum L.) collected from high mountain pastures in northeast Anatolia (Turkey) were examined fo

94 ce of secondary forests growing on abandoned pastures in the wet subtropical forest life zone of Puer

95 mid-latitude natural forests to cropland and pastures is accompanied by an increase in the occurrence

96 tors highlight that cold-trapping of POPs in pastures is mostly due to increased gas-phase deposition

97 Against Allergy Study in Rural Environments (PASTURE) is a European birth cohort where pregnant women

98 s of the new vegetation (tree plantations or pastures), its age, and precipitation.

99 Crop and pasture land has replaced their forest habitat, and huma

100 ing example is that of overgrazing of common pasture lands.

101 nthelmintics combined, where practical, with pasture management.

102 ion averaged twice the size of clearings for pasture (mean sizes, 333 and 143 ha, respectively), and

103 ic milk (n=10), conventional milk (n=14) and pasture milk (n=20) from winter (n=22) and summer (n=22)

104 d and offered ad libitum access to fresh cut pasture of three different types, varying in digestibili

105 a limited fraction of all cow pats end up on pastures, offering limited scope for dung beetle mitigat

106 Picture a pasture open to all (...) As a rational being, each herd

107 When forests are replaced by pasture or crops, evapotranspiration of moisture from so

108 Iberian ham from pigs fattened on acorn and pasture or on feed.

109 de zones, two aspects, and were either sheep pasture or ungrazed meadow.

110 < 0.01) of SOC changes observed after sowing pastures or planting trees.

111 The replacement of native vegetation by pastures or tree plantations is increasing worldwide.

112 large (>25-ha) clearings as cropland, cattle pasture, or regrowing forest in the years after initial

113 ietary treatments fed over a 1 year period : pasture (P), barley-based concentrate (C), silage follow

114 New Zealand to show that parasitism of a key pasture pest (Listronotus bonariensis; Argentine stem we

115 arch of importance to understanding crop and pasture plant species response to climate change.

116 Global croplands, pastures, plantations, and urban areas have expanded in

117 from the intake of beta-carotene present in pasture plants, was found in milk and cheese.

118 he tolerant mine populations and nontolerant pasture populations.

119 ominating botanical families in the mountain pasture prevailed in the sheep diet of the commercial fl

120 We studied the rural birth cohort PASTURE (Protection against allergy: study in rural envi

121 ent, these changes will lead to a decline in pasture quality and increase the risk from tick-borne di

122 Pasture remains the dominant land use after forest clear

123 e vertical distribution of SOC occurred when pastures replaced native forests, with SOC gains in the

124 In Brazilian soils, almost all pasture samples preferentially transformed the non-herbi

125 e spectra was respectively 0.96 and 0.91 for pasture samples, and 0.96 and 0.79 for preserved-forage

126 ey-based concentrate (C), silage followed by pasture (SiP) or silage followed by pasture with concent

127 ltaneous atmospheric soundings at forest and pasture sites during the Rondonian Boundary Layer Experi

128 establishment of soil surface communities on pasture soil in microcosms exposed to light or dark cond

129 ifferent locations (coniferous forest soils, pasture soils and agricultural soils) and discuss how va

130 d solubility and plant uptake in New Zealand pasture soils.

131 The setting was the PASTURE study, a multicenter prospective birth cohort st

132 mple of French and Finnish children from the PASTURE study.

133 Against Allergy-Study in Rural Environments (PASTURE) study followed 1133 children living in rural ar

134 nal traits of stingless bee species found in pastures surrounded by differing amounts of forest in an

135 New pasture taxa (including species, subspecies, varieties,

136 ucing novel genetic and endophyte variation, pasture taxa are imbued with additional capacity for inv

137 few governments regulate conventionally bred pasture taxa to limit threats to natural areas, even tho

138 duce environmental risks associated with new pasture taxa.

139 Within a pasture, TBA-implanted heifers (40 mg TBA, 8 mg estradio

140 show that cloud base heights are higher over pasture than over tropical forest areas under reasonable

141 ata trees in a continuous forest to those in pasture through microsatellite-based paternity analysis

142 ple habitat types, including crop fields and pastures (to which 15% of species are restricted), altho

143 There was more inbreeding within pasture trees (outcrossing=0.828+/-0.015) compared with

144 Pasture trees had fewer sires contributing to mating eve

145 ich was reflected in the selfing rates among pasture trees shown by the paternity analysis (0-80% sel

146 showed variation in outcrossing rates among pasture trees with high proportions of external and self

147 eding regimes (especially grazing intake and pasture type) on milk fatty acid (FA) profiles.

148 were also positive but weaker, regardless of pasture type.

149 est at lower elevations to warmer deforested pastures upslope.

150 cheese samples from different regimes (here, pasture vs. preserved-forage).

151 Cattle pasture was badgers' most preferred habitat.

152 Results show that pasture was the primary driver of biodiversity loss in M

153 Linoleic acid in pastures was highest in the second phase which coincided

154 f nine male Romane lambs grazing a cocksfoot pasture were supplemented with different levels of fresh

155 lowed by pasture (SiP) or silage followed by pasture with concentrate (SiPC).

156 ennial, cool-season forage species grown and pastured worldwide.

157 ensitivity analysis showed that the cropland-pasture yield elasticity and the choice of the land use