ライフサイエンスコーパス: park

1 ransportation (OR, 0.13; 95% CI, 0.03-0.49), parks (OR, 0.09; 95% CI, 0.01-0.88), and maintained vaca

2 rsity of 576 Adineta vaga individuals from a park in Belgium.

3 e, rainwater sedimentation pond, a pond in a park, and a wadi, were assessed.

4 tranger whom they imagined encountering on a park bench.

5 A parking strategy is often ideal in the early stages of a

6 eas the endoplasmic reticulum may serve as a parking lot for this enzyme.

7 and the distribution of gap sizes left by a parking strategy.

8 ure of tightly stacked ER sheets resembles a parking garage, in which the different levels are connec

9 h the hydrophobic loop could be locked in a "parked" conformation by a disulfide bond between C180 an

10 lution, the loop resides predominantly in a "parked" position within the filament but is able to dyna

11 The additional park use and park-based physical activity occurred not o

12 of walkability, public transport access, and park access were assessed in 1.0 km and 0.5 km street ne

13 ed systematically to document facilities and park users by age group and sex.

14 uld potently suppress pathology in Pink1 and park mutants.

15 E-BP and was also able to suppress Pink1 and park pathology.

16 The additional park use and park-based physical activity occurred not only on the wa

17 Park features also influence park use and park-based physical activity.

18 ise exposures, neighborhood walkability, and park proximity.

19 -actin, fluctuating between the extended and parked conformations.

20 in 3 microL; 15 mM, 45 nmol) is injected and parked in the probe to yield a heteronuclear multiple-qu

21 erse particle samples--soil, urban dust, and parking deck sweepings--were fractionated using this tec

22 lated financial outlays included: travel and parking associated with hospital appointments; costs of

23 oprene concentrations over urban forests and parks by 0.6-1.4 ppbv.

24 ailability of public transit, sidewalks, and parks were characterized for the residential neighborhoo

25 nd hot dogs in street medians (24 sites) and parks (21 sites) in New York City, USA.

26 engaging urban planning, transportation, and parks sectors in efforts to reduce the health burden of

27 fe (Giraffa camelopardalis) in a wild-animal park in the United States.

28 eath of a captive beluga whale in an aquatic park.

29 Fractions are parked in the reactor where they undergo complete dephos

30 y providing food or refuge for rats, such as parks.

31 loops, and a particular analyte band can be parked in one NMR detector coil while CE continues in th

32 e apoptosome and one catalytic domain may be parked on the hub, when an odd number of zymogens are bo

33 istory of illegal harvest and enforcement by park authorities.

34 s very difficult; most sites are obscured by parked cars.

35 spontaneous graft tolerance was restored by parking the irradiated LEW donor liver in naive LEW rats

36 (for example, finding the car in a busy car park) and animals (for example, foraging for food).

37 y the side of a road in the presence of cars parked at random along the road.

38 In addition, KJ1.26(+) HSV nonimmune cells parked in ocularly infected BALB/c mice were demonstrabl

39 th serologically and virologically in a city park of Jiangxi in 2009.

40 irectly from DNA isolated from New York City park soils.

41 ison of sequences derived from New York City parks to genes involved in the biosynthesis of biomedica

42 lly covering the loading bay prevent correct parking of the truck.

43 Drosophila double park encodes a homolog of Cdt1 that functions in initiat

44 We identified a Drosophila gene, double parked (dup), that is essential for DNA replication and

45 mpletely suppressed by cosilencing of Double parked (Dup), the Drosophila homologue of Cdt1, a replic

46 he pre-replication complex component, double-parked protein/cell division cycle 10-dependent transcri

47 We find that increased Double-parked (Dup), the Drosophila ortholog of Cdt1, results i

48 gated the developmental regulation of Double-parked (Dup) protein, the Drosophila ortholog of Cdt1, a

49 ination of other ORC members, whereas Double-parked protein/Cdt1 and minichromosome maintenance prote

50 rs that genetically interact with Drosophila park and Pink1.

51 by the following driving environments: empty parking lots, suburban residential streets, intermediate

52 sferred into MHC class II-deficient mice for parking, and the hosts were later analyzed for long-live

53 g of samples from North Island native forest parks identified a widespread population of Saccharomyce

54 robability that the loading bay is free from parked cars.

55 Even uninhabited frontier parks are logged to supply international markets.

56 ack-a-mole" sensitivity, after a popular fun park game.

57 treet trees, green roofs, community gardens, parks and open spaces, and extensive connective pathways

58 e evaluate the feasibility of using hospital parking lot traffic data extracted from high-resolution

59 A hybrid parking strategy has been employed for portions of the H

60 crisis, and molecular genetics can assist in park design by helping to identify key species, historic

61 t difficult driving tasks were navigating in parking ramps, parking in the correct space, seeing lane

62 ber of people and their physical activity in parks with and without walking loops, controlling for mu

63 Arthropod diversity was greater in parks (on average 11 hexapod families and 4.7 ant specie

64 Here we describe the use of walking loops in parks and compare the number of park users and their phy

65 k on streets and sidewalks, walking loops in parks offer a setting to walk in nature and to avoid int

66 -3 times more food per day than did those in parks.

67 controlling for multiple factors, including park size, facilities, and population density.

68 d from residential areas close to industrial parks in central Taiwan were analyzed.

69 Park features also influence park use and park-based physical activity.

70 ted nature of the gaps left after an initial parking strategy may make it difficult to finish a proje

71 Ion parking was used to increase the number of parent ions o

72 tion events interspersed with additional ion parking ion/ion reaction periods were used to "charge-st

73 These include an ion parking experiment for the purpose of gas-phase ion conc

74 n of proton transfer reactions (PTR) and ion parking on an Orbitrap mass spectrometer.

75 Using PTR and ion parking, we evaluate the charge state dependence of frag

76 mass-to-charge ratios is referred to as "ion parking".

77 r ion/ion reactions under a given set of ion parking conditions.

78 Parallel ion parking is demonstrated with a six-component protein mix

79 range, in a process termed HALF parallel ion parking.

80 PTR/ion parking allows charge states of proteins to be focused i

81 The efficiency and specificity of the ion parking experiment is highly dependent upon ion densitie

82 The ion parking experiment is illustrated herein along with appl

83 on/ion proton-transfer reactions and the ion parking technique were applied to purify and concentrate

84 njunction with mass-to-charge dependent ion "parking" to accumulate protein ions initially dispersed

85 We suggest that the converted state is "park," in which kinetochores are anchored to plus ends o

86 waterfowl, including ducks, in two Hong Kong parks.

87 Our discussion includes modified parking strategies and hybrids with other strategies.

88 at these binding sites comprise a "molecular parking lot" in which the AChE molecules can be released

89 GP), a durable, solar-powered air monitoring park bench that measures real-time ozone, PM2.5, and met

90 ulation of wild baboons living in a national park in Kenya.

91 ienced recruitment failure within a national park, now surrounded by logged forest.

92 ed growth for each wilderness area, national park, and national forest in the conterminous United Sta

93 as (prey-rich vs. prey-poor) of the national park.

94 National parks and bioreserves are key conservation tools used to

95 raits of large mammal species in 13 national parks in Kenya over the past 60 y.

96 occurrence are found over state and national parks in the southeast during winter and spring, in the

97 rances to major attractions such as national parks.

98 and cattle collected from biobanks, national parks, and other regions of South Africa were used in du

99 pecies are rare in long-established national parks and nature reserves, which are actively protected

100 ing 2008-2010 from 17 lakes in four national parks of the northwestern Laurentian Great Lakes region.

101 onomic conservation success at four national parks, four comanaged reserves, and three traditionally

102 fine particulate matter and haze in national parks and wilderness areas where visibility is protected

103 ections, ranging from 25 to 100% in national parks.

104 ity hotspots worldwide and two U.S. national parks (Cuyahoga and Rocky Mountain).

105 experienced in eight selected U.S. national parks if climate change causes mammalian species within

106 nd drastic influxes of new species, national parks are not likely to meet their mandate of protecting

107 much the same way that traditional national parks preserve special geological features and historica

108 ood walkability, and distance to the nearest park.

109 nce and use of walking loops in neighborhood parks: a national study.

110 hich a representative sample of neighborhood parks (n = 174) from 25 U.S. cities with > 100,000 popul

111 Access to neighborhood parks may increase levels of physical activity and reduc

112 heir physical activity in urban neighborhood parks with and without walking loops.

113 ps, on average during an hourly observation, parks with walking loops had 80% more users (95% CI: 42,

114 tional conservation programs and an index of park-related funding.

115 ing loops in parks and compare the number of park users and their physical activity in urban neighbor

116 the availability and increasing the cost of parking, designing pedestrian-friendly and cycling-frien

117 It is akin to the problem of parking a truck at a loading bay by the side of a road i

118 reat uncertainty about the future ability of parks and protected areas to meet their conservation man

119 nding would directly increase the ability of parks to protect tropical biodiversity.

120 We found that the majority of parks are successful at stopping land clearing, and to a

121 .037 [1.018-1.056]; p=0.0007), and number of parks (1.146 [1.033-1.272]; p=0.010).

122 munities, possibly because vegetation in old parks have had a longer time to modify soil properties a

123 dely used in the central and eastern U.S. on parking lots, driveways, and even playgrounds, are typic

124 le assembling into a "hub" or "platform" or "park" the various companies and services that link farme

125 Therefore, in addition to our parking model, we model gap closing by walking.

126 ard highly protected areas and ignore "paper parks." Analysis of a Brazilian database does not suppor

127 Apparently there are marine 'paper parks' just as there are terrestrial 'paper parks'.

128 parks' just as there are terrestrial 'paper parks'.

129 freeway (12%), in the rain (9%) and parallel parking (8%).

130 ermittent voltage drops, also known as "peak parking," and analyzed by collision-induced dissociation

131 The capability of the monolith to do peak parking experiments was demonstrated by the characteriza

132 standards were also measured, using the peak parking method.

133 time on selected fractions, similar to "peak parking".

134 As a project progresses, parking becomes progressively more expensive and eventua

135 uld provoke a different response at a public park than a shooting range.

136 ving tasks were navigating in parking ramps, parking in the correct space, seeing lane markings, and

137 in mortality among waterfowl in recreational parks, domestic flocks, and wild migratory birds.

138 c samples that were collected in a recycling park (manufacture date before 2006), this suggests a rec

139 st are sampled into loops, where they remain parked until their sequential reinjection onto the secon

140 hus, despite increasing densities in smaller parks, we conclude that there are only two robust popula

141 of solar parks, optimal connections of solar parks across time zones for minimizing intermittency, an

142 apacity and storage, optimal siting of solar parks, optimal connections of solar parks across time zo

143 ecreation services generated by the US state park system is approximately $14 billion annually.

144 ecreation services generated by the US state park system.

145 All state parks generate annually an estimated 2.2 billion hours o

146 ith information on the availability of state parks and other potentially important drivers of recreat

147 , the approximately 2 million acres of state parks established between 1975 and 2007 are estimated to

148 sed to examine the net contribution of state parks to nature recreation.

149 The results show that state parks have a robust positive effect on nature recreation

150 of GroEL: the ability to act as a temporary parking spot for sticky intermediates by binding many mo

151 We show that park age shaped the composition of microbial communities

152 opical countries to test the hypothesis that parks are an effective means to protect tropical biodive

153 to reside in Gabon [1], their loss from the park is a considerable setback for the preservation of t

154 ), while the ratio in surface soils from the park was typically an order of magnitude lower.

155 1.1 x 10 degrees mug/L), and the pond in the park (2.9 x 10(1) mug/L), where low levels of microcysti

156 We assessed population change in the park and its surroundings between 2004 and 2014.

157 None of the other snakes in the park was moribund, and RT-PCR results for surveillance s

158 other rather than from other reptiles in the park, with subsequent interanaconda juvenile transmissio

159 esence of poor households at the edge of the park does not signal that the park is a poverty trap.

160 In the interior of the park, adult survival was less variable and density-indep

161 ession in the prey-rich northern area of the park.

162 ent with our findings in the interior of the park.

163 although the poor tend to be located on the park perimeter, proximity to the park has no measureable

164 However, a bad decade for forest outside the park proved a prosperous one for most local residents.

165 he edge of the park does not signal that the park is a poverty trap.

166 63 long-term monitoring sites throughout the park.

167 only on the walking loops but throughout the park.

168 for boys, more frequent family visits to the park (-1.89; -3.28, -0.51) and family participation in s

169 itions collected from a site adjacent to the park during August-October 2012 was 96 Bq mg(-1), while

170 ated on the park perimeter, proximity to the park has no measureable effect on growth of productive a

171 s inversely correlated with proximity to the park, initial farm size, and decline in adjacent communa

172 The parking strategy is an iterative approach to DNA sequenc

173 m ligand binding prior to elimination of the parking problem but also extended that treatment to incl

174 ak of salmonellosis in a large Florida theme park.

175 patients had drunk orange juice in the theme park vs 54% of controls (matched odds ratio, undefined;

176 l study, case patients were limited to theme park hotel visitors and controls were matched to case pa

177 oliferation, yet timing and insensitivity to park mutation suggest that preferential proliferation un

178 (PAHs) in living spaces and soil adjacent to parking lots sealed with coal-tar-based products.

179 e dust in living spaces and soil adjacent to parking lots sealed with coal-tar-based products.

180 Urban trees, parks, gardens, open spaces, and other nearby nature ele

181 eet in London (Oxford Street) or in an urban park (Hyde Park).

182 eptides and polyketides, we found that urban park soil microbiomes are both rich in biosynthetic dive

183 pared soil microbial communities in 41 urban parks of (i) divergent plant functional types (evergreen

184 th bacterial and fungal communities in urban parks responded to plant functional groups, but fungi we

185 that, despite frequent disturbances in urban parks, urban soil microbes still followed the classic pa

186 iverse soil microbial communities than urban parks that are under continuous anthropogenic disturbanc

187 racterized by heavy traffic and within urban parks.

188 interest from the IEF dimension, as IEF was 'parked' during each CE analysis and refocused prior to a

189 ithout Ag also served as memory T cells when parked for 100 d in unirradiated, syngeneic recipients w

190 Overall, compared with parks without walking loops, on average during an hourly

191 te of protecting current biodiversity within park boundaries.

192 ties and microbial communities than in young parks.

193 aths of several exotic birds at a zoological park in the same area.

194 ons of species might differ, most zoological parks worldwide commonly feature mixed-species exhibits.