ライフサイエンスコーパス: shore

1 p to 2 kb distant, which we term 'CpG island shores'.

2 area of 1100 m (alongshore) by 440 m (cross-shore).

3 phate, and silicate, respectively, along the shore.

4 ng stations 300 m offshore than close to the shore.

5 been considered within a few kilometers from shore.

6 1.8 (95% CI: 1.2, 2.7) for the Upper Eastern Shore.

7 he shell-core transition zone, the so-called shore.

8 s conducted along Lake Malawi's southwestern shore.

9 extended about 30 km beyond its present-day shore.

10 structure of subtidal communities closer to shore.

11 II) concentrations (up to about 120 nM) near shore.

12 summer on the sea ice or, where it melts, on shore.

13 er deposition, but were near equilibrium off-shore.

14 he upper water column and/or lived closer to shore.

15 tem (GPS) time series at stations located on shore.

16 tebrate inhabiting North Atlantic intertidal shores.

17 derstanding heat stresses - rocky intertidal shores.

18 t of which overlap with genes and CpG island shores.

19 adients between temperate and tropical rocky shores.

20 zers, as these underpin the ecology of rocky shores.

21 hinder evolving hurricanes from reaching US shores.

22 t structures biodiversity in temperate rocky shores.

23 e intertidal communities along Iberian rocky shores.

24 y located in areas distal to CpG islands and shores.

25 actors and are distinct from CpG islands and shores.

26 more likely to overlap with CpG islands and shores.

27 collected at the microhabitat level, from 15 shores along the Atlantic European coast spanning nearly

28 inental shelf-break but are also common near-shore and 2) in impacted areas, lionfish have reduced to

29 ross elevation gradients, with distance from shore and among habitat and vegetation types.

30 se states varied by vertical position on the shore and appear to be driven by microhabitat conditions

31 tivity is shaped by sodium toxicity near the shore and by sodium deficit farther inland.

32 5alpha-THP labeling in the nucleus accumbens shore and central nucleus of the amygdala, independent o

33 decades, it has yet to be documented in near-shore and coral reef environments.

34 nes in activity and body temperature of both shore and ice bears in summer, resembling energy expendi

35 ical bottleneck', inhabited exclusively near-shore and marine environments; and third, the evolution

36 ferential methylation of probes lying in the shore and shelf and enhancer regions of striatal and cer

37 Spat collection efforts from shore and within the water column were unsuccessful; thi

38 G islands from the UCSC database, CpG island shores and additional content selected from whole-genome

39 ry regions such as promoter CpG islands, CpG shores and enhancers show changes in methylation during

40 t DNA methylation of CpG islands, CpG island shores and first exons is known to play a key role in th

41 on; survival was predicted for two different shores and four sampling times using a single recruitmen

42 represented in regions flanking CpG islands (shores and shelves) and gene bodies.

43 h as those surrounding the CpG islands, i.e. shores and shelves.

44 cerebellum samples, enriched in CpG island "shores" and at further distances from CpG islands.

45 B ALL subtypes, and methylation in CGIs, CGI shores, and in regions around the transcription start si

46 single-base resolution confirm that sloping shores are universal for hypomethylated CGIs in sperm an

47 ng from human use of arctic coastal and near-shore areas as sea ice diminishes.

48 treatment upgrades to the most affected near-shore areas, while simultaneously implementing legislati

49 d wave fetch (a measure of the exposure of a shore) as explanatory variables.

50 angles between the wave crest lines and the shore, as has been demonstrated in shoreline models.

51 n minimum zone and not depth or proximity to shore, as might be expected.

52 r personnel in dry dock; and 6.9% (9/131) of shore-based female naval personnel in San Diego.

53 enlisted men; 5.2% (21/406) of male marines shore-based in Okinawa, Japan; 2.7% (5/183) of female en

54 Shore-based sampling revealed that between-site differen

55 iology of "ice" bears in summer is unknown, "shore" bears purportedly minimize energy losses by enter

56 decline has ecological consequences for near shore benthic ecosystems.

57 e to a redirection of production to the near-shore benthic zone, and large lakes may exhibit shifts i

58 king regions of active promoters, CpG island shores, binding sites of the transcription factor CTCF a

59 ations of waterfowl, breeding, and migratory shore birds.

60 showed that differential methylation of CGI shores, but not CGIs, significantly regulated Cav1 expre

61 ough December 2011 at the Mass General/North Shore Cancer Center, a community-based cancer center in

62 ression pattern of genes associated with CGI shore cDMRs was able to discriminate between disease phe

63 predator attack, foraging unusually close to shore, chemical or algal toxin exposure, abnormal weathe

64 ncipal investigators, and more companies off-shoring clinical trials, overcoming such barriers is of

65 ater, reduced subsurface oxygen both in near-shore coastal water and in the open ocean, rising coasta

66 ean 7.8-7.9, minimum 7.4-7.5), typical rocky shore communities with abundant calcareous organisms shi

67 res of primary production from near- and off-shore communities.

68 ny predator species per prey species as near-shore communities.

69 ere, we removed sessile species from a rocky shore community in a way that deliberately mimicked natu

70 le outplants was reduced dramatically at mid shore compared to low shore levels regardless of the pCO

71 , a phenomenon that we described as "sloping shores." Computational analyses of human and mouse methy

72 cific and density-dependent effects of rocky shore consumers (crabs and snails) on community recovery

73 On 16 March, on-shore continuous GPS stations detected a westward motion

74 rom the south and those living higher on the shore coping better with stressful conditions.

75 e fixed-effects summary odds ratio was 1.35 (Shore-corrected 95% confidence interval: 1.23 to 1.47),

76 eciprocity between epigenetic markers at CGI shores corresponding to differential gene expression in

77 ong 40 km of NW Mediterranean subtidal rocky shores (Corsica, France).

78 Here, we test the hypothesis that the shore crab (Carcinus maenas) can take up microplastics t

79 ze on a community comprised of the predator (shore crab Carcinus maenas), various grazing detritivore

80 oplastics may be ingested and inhaled by the shore crab Carcinus maenas, although the biological cons

81 ctory predator cues (Carcinus maenas, common shore crab).

82 ence of the minor form of CHH from the green shore crab, Carcinus maenas, was determined by automated

83 outhern New England (USA) the invasive Asian shore crab, Hemigrapsus sanguineus, preys on mussels (My

84 e to human antidepressant drugs; the striped shore crab, Pachygrapsus crassipes, was studied using an

85 n of serotonin than is aggressiveness in the shore crab.

86 conditions using behavioural bioassays with shore crabs (Carcinus maenas) as a model system.

87 compared to the physiological resilience of shore crabs in maintaining osmoregulatory and respirator

88 e hemiellipsoid body (HB) of the eyestalk of shore crabs.

89 A simulation study based on CpG Shore data suggested that in terms of detection of diffe

90 high-dimensional methylation data sets (CpG Shore data, THREE data and NIH Roadmap Epigenomics data)

91 se inhibitor induced Cav1 expression via CGI shore demethylation.

92 Finally, by tracing sloping shore dynamics through embryonic and germ cell reprogram

93 A new study on rocky shore ecosystems now offers a test of warning indicators

94 the highest activities associated with near-shore eddies and the Kuroshio Current acting as a southe

95 ise over 14 degrees of latitude and 1 m of shore elevation.

96 ethylation was overrepresented in CpG island shores, enriched within gene bodies but not in intergeni

97 the GOE there was pervasive suboxia in near-shore environments, allowing nonquantitative Se reductio

98 Lower shore epiphytes were dominated by filamentous diatoms (B

99 Upper shore epiphytes were dominated by green algae (Chlorophy

100 ave evaluated the effects of the oil on near-shore estuarine fish species such as red drum (Sciaenops

101 Eleanor and Miles Harvard Medical School Shore Fellowship Grant, and Massachusetts General Hospit

102 mass of aerosols arriving at North American shores from overseas is comparable with the total mass o

103 mulative ecosystem stress is highest in near-shore habitats, but also extends offshore in Lakes Erie,

104 ht environment resulting from differences in shore height and shading within the host macroalga, like

105 ne and after 1, 3, 6, and 12 months at North Shore Hospital.

106 with Cav1 CGI shore methylation levels, with shore hypermethylation in minimally aggressive, luminal

107 aggressive, luminal breast cancer cells and shore hypomethylation in highly aggressive, basal-like c

108 all ponds, lakes, streams/rivers and the sea shore (i.e. downward QH), with Tw-Ta becoming increasing

109 ake greater use of habitat that is closer to shore in relation to senescent-aged moose.

110 nter to summer, (iii) and with distance from shore in surface waters only.

111 On rocky shores in Maine, recent experiments suggest that recover

112 n of cytosine-phosphate-guanine (CpG) island shores in nine human iPS cell lines as compared to their

113 ns were situated along the Jubbah palaeolake-shores, in a grassland setting with some trees.

114 ns, ocean geology, and remote control of off-shore industrial activities.

115 d for marine environmental monitoring of off-shore industrial sites.

116 g y(-1) (of mainly higher congeners) to near-shore Lake Ontario compared with volatilization of appro

117 he main route of Sigma5PBDE loadings to near-shore Lake Ontario which acts as a net PBDE sink.

118 tiple private and public values on its North Shore land holdings (Island of O'ahu) of approximately 1

119 However, given the large Mediterranean shore length relative to its surface area, SGD may be a

120 ion between the larval carry-over effect and shore level, suggesting little modulation of acidificati

121 ed dramatically at mid shore compared to low shore levels regardless of the pCO2 level that oysters e

122 gh juveniles grew less at mid shore than low shore levels, there was no evidence of an interaction be

123 ion of Infectious Disease Diagnostics, North Shore-LIJ Health System, and now is Vice President for G

124 ication of terrestrial, freshwater, and near-shore marine ecosystems, and comparable increases in pes

125 ith major implications for riverine and near-shore marine environments.

126 nd Women's, Massachusetts General, and North Shore Medical Center) were evaluated for CMS reporting s

127 adjusted confidence interval (CI) using the Shore method of 95% CI [1.02, 1.45].

128 Recently, other patterns such as CpG island shore methylation and long partially hypomethylated doma

129 hat the increase is a byproduct of island or shore methylation followed by deamination.

130 ncer aggressiveness associated with Cav1 CGI shore methylation levels, with shore hypermethylation in

131 Cav1 CGI shore methylation was also observed in human breast tumo

132 CpG island shore methylation was strongly related to gene expressio

133 rst study of Cav1 (a potential oncogene) CGI shore methylation, we suggest this phenomenon may repres

134 rst study of Cav1 (a potential oncogene) CGI shore methylation, we suggest this phenomenon may repres

135 , and pore-water nutrients) on an intertidal shore near Dublin, Ireland.

136 eastern United States are most prevalent off-shore near the continental shelf-break but are also comm

137 Early invasions of the North American shore occurred mainly via deposition of ballast rock, wh

138 present-day sea level along the southeastern shore of Bermuda contain remains of a former breeding co

139 ocated above the head-of-tide on the western shore of Chesapeake Bay.

140 fibrosis is common in communities along the shore of Lake Albert.

141 ient particles collected on the southeastern shore of Lake Michigan during an event (July 6-8, 2015)

142 ranged from <DL to 2.6 ng/L on the southern shore of Lake Ontario near the mouth of the Oswego River

143 pitation samples were collected close to the shore of Lake Victoria at Entebbe, Uganda, between Octob

144 seawater of Kaneohe Bay on the northeastern shore of Oahu, Hawaii, by extinction culturing in seawat

145 the food chain in shelf waters off the west shore of Oahu, Hawaii.

146 River and adjacent waterways on the eastern shore of the Chesapeake Bay in Maryland, USA.

147 Bioinformatics analysis revealed a CpG shore of the CNTFRalpha gene regulated its mRNA expressi

148 heir roots in the populations on the eastern shore of the Mediterranean Sea.

149 e organisms of drift debris deposited on the shores of 30 remote islands from the Arctic to the Antar

150 Flow depths along the shores of Banda Aceh exceeded 9 meters, with inundation

151 a) and Brassica crop species, thrives on the shores of Lake Tuz, Turkey, where soils accumulate high

152 Tar balls collected from the Gulf of Mexico shores of Louisiana and Florida after the BP oil spill h

153 f kilometers across the Pacific Ocean to the shores of North America and Hawai'i.

154 amples were collected at five sites near the shores of the Great Lakes during the period 2008-2009, i

155 ir samples collected from six sites near the shores of the Great Lakes.

156 amples collected at five sites, all near the shores of the North American Great Lakes during 2008-200

157 protein 2 to the "cytosine-phosphate-guanine shores" of the Kcc2 promoter, and decrease in binding of

158 ntries around the Mediterranean Sea with off shore oil production.

159 , but rather in the 3' UTR, gene bodies, CpG shores or 'offshore' sites, and both positive and negati

160 t enrichment of hypermethylated cDMRs in CGI shores (P < 10(-60)), non-CGI-associated promoters (P <

161 rpendicular erosion and 11 m for the maximum shore-perpendicular accretion during the study period.

162 The horizontal, shore-perpendicular change in shoreline position along t

163 we find upper limits of 25 m for the maximum shore-perpendicular erosion and 11 m for the maximum sho

164 n position of the 0.8-m contour sampled from shore-perpendicular profiles spaced at 20-m intervals al

165 ears of monthly profile surveys taken at two shore-perpendicular transects at Duck, North Carolina, U

166 growth patterns in the western central near-shore portion of Second Connecticut Lake, Pittsburg, New

167 rths at U.S. ports that could be switched to shore power to yield the largest gains for society.

168 NOX, SO2, PM2.5, and CO2 that would occur if shore power were used.

169 require many ships to be equipped to receive shore power, even if doing so would result in a private

170 ves and mandates to encourage a shift toward shore power.

171 thin promoter 'CpG islands' (CGIs) with 'CGI shores', recently described regions that flank CGIs with

172 n due to hyper-methylation in the CpG island shore region of mmu-miR-15b in both the spermatozoa of F

173 osystems is more recent in oceanic than near shore regions, yet our understanding of human impacts on

174 The sample locations comprised shore sediment of a large European river (Rhine) and a r

175 cation of pellets, which were separated from shore sediment samples of both rivers.

176 Along shore sediment transport that is driven by waves is gene

177 For this reason, river shore sediments of the rivers Rhine and Main in the Rhin

178 wrinkles are preserved in barely bioturbated shore-shallow lacustrine siliciclastic deposits of the L

179 hylation in CpG islands and demethylation at shore/shelf and open sea.

180 00), 1st exons, 5'UTRs, 3'UTRs, CpG islands, shores, shelves, open seas and FANTOM5 enhancers.

181 cies responses (for example, changes in near-shore species abundance and predator absence).

182 nced clones revealed that G. duebeni, a high-shore species with the highest thermal tolerance, expres

183 The Mediterranean shores stretching between Sicily, Southern Italy and the

184 The marine shore sulfidic mine tailings dump at the Chanaral Bay in

185 ement for both species, coincident with near-shore surface currents.

186 compare ecological shifts in subtidal rocky shore systems along CO2 gradients created by volcanic se

187 require a fine-scale assessment of the near-shore temperature changes.

188 Although juveniles grew less at mid shore than low shore levels, there was no evidence of an

189 gene expression more strongly at CpG island shores than CpG islands.

190 DM loci occurred twice as frequently in the shores than in the actual CpG islands.

191 On the Upper Eastern Shore, the IRR for arthritis reversed, indicating higher

192 On New Zealand rocky shores, the magnitude of such subsidies differs profound

193 occurs outside of CpG islands and CpG island shores, thus rejecting the hypothesis that the increase

194 habitats ranging from shallow water, to near shore to the open ocean and the deep sea.

195 case study of one measurement drive from the shore to the precoastal mountain range furthest downwind

196 cal study was carried out in Rumonge, a lake-shore town where 318 people were admitted to hospital wi

197 fic work has proceeded in a robust manner to shore up the validity of APS as a diagnostic construct.

198 Choosing to shore up those rights, however, will increase the number

199 onger increase in peak- and late-season near-shore upwelling in the northern limb of the California C

200 onger decrease in peak- and late-season near-shore upwelling in the southern limb.

201 reported for the first time floating in off-shore waters.

202 icinalis on upper and lower zones of a rocky shore were determined.

203 t geographic region, depth, and proximity to shore were significant predictors of community structure

204 Gene bodies, intergenic regions, and CpG shores were preferentially demethylated during erythropo

205 nd other variables (salinity and distance to shore) were much weaker.

206 n its focus of endemicity, the Upper Eastern Shore, were calculated.

207 ion by turbulent shear typical of wave-swept shores where adults of this species live.

208 pment of oscillatory biological reactions at shores where waves impinge on rocks and bring nutrients

209 ithin about 100 km), narwhal moved closer to shore, where they were presumably less vulnerable.

210 s significantly enriched in CpG island (CGI) shores while depleted in CGIs themselves, especially in

211 te concentrations yield maximal biomass near shore, while offshore biomass is positively correlated w

212 combined cycle (without CO2 capture) and on-shore wind power plants, both from a levelized and margi

213 Its genomic location, a CpG island shore within an H3K27ac enhancer mark, and the correlati

214 g to show that subsea permafrost in the near-shore zone of the ESAS has a downward movement of the ic

215 Beyond the near-shore zone, these regions typically have a carbonate con