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1 p to 2 kb distant, which we term 'CpG island shores'.
2 area of 1100 m (alongshore) by 440 m (cross-shore).
3 structure of subtidal communities closer to shore.
4 II) concentrations (up to about 120 nM) near shore.
5 summer on the sea ice or, where it melts, on shore.
6 er deposition, but were near equilibrium off-shore.
7 he upper water column and/or lived closer to shore.
8 tem (GPS) time series at stations located on shore.
9 ng stations 300 m offshore than close to the shore.
10 , primarily within 30 km of the southeastern shore.
11 de contents decreased with distance from the shore.
12 been considered within a few kilometers from shore.
13 1.8 (95% CI: 1.2, 2.7) for the Upper Eastern Shore.
14 he shell-core transition zone, the so-called shore.
15 s conducted along Lake Malawi's southwestern shore.
16 are associated with different heights on the shore.
17 ly-generated eddies extends for 1000 km from shore.
18 phate, and silicate, respectively, along the shore.
19 extended about 30 km beyond its present-day shore.
20 e intertidal communities along Iberian rocky shores.
21 y located in areas distal to CpG islands and shores.
22 actors and are distinct from CpG islands and shores.
23 more likely to overlap with CpG islands and shores.
24 tebrate inhabiting North Atlantic intertidal shores.
25 t of which overlap with genes and CpG island shores.
26 adients between temperate and tropical rocky shores.
27 zers, as these underpin the ecology of rocky shores.
28 in promoters located outside CpG islands and shores.
29 hinder evolving hurricanes from reaching US shores.
30 ade, particularly on O 'ahu's north and west shores.
31 nding sites within their promoter CpG island shores.
32 t structures biodiversity in temperate rocky shores.
33 derstanding heat stresses - rocky intertidal shores.
34 nces in coral reefs, kelp forests, and rocky shores.
35 espond to concerns expressed by Pacifici and Shore (2019) about a recent paper (Lees-Shepard and Gold
36 ridula along the south-eastern Pacific rocky shore (30 degrees S, Chile) in the region occupied by th
37 blend of pigments for incorporation into the Shore 40 silicone elastomer to generate a prosthesis tha
38 most common forms of contamination impacting shores after a major oil spill; and following the Deepwa
39 collected at the microhabitat level, from 15 shores along the Atlantic European coast spanning nearly
40 inental shelf-break but are also common near-shore and 2) in impacted areas, lionfish have reduced to
42 se states varied by vertical position on the shore and appear to be driven by microhabitat conditions
44 5alpha-THP labeling in the nucleus accumbens shore and central nucleus of the amygdala, independent o
48 nes in activity and body temperature of both shore and ice bears in summer, resembling energy expendi
50 lti-scale processes (e.g., wave-driven cross-shore and longshore transport; dune, bluff, and cliff er
51 ical bottleneck', inhabited exclusively near-shore and marine environments; and third, the evolution
52 ferential methylation of probes lying in the shore and shelf and enhancer regions of striatal and cer
53 opper and aluminum due to large distances to shore and thus incurs higher embodied CO(2)-eq per MWh.
56 G islands from the UCSC database, CpG island shores and additional content selected from whole-genome
57 ry regions such as promoter CpG islands, CpG shores and enhancers show changes in methylation during
58 t DNA methylation of CpG islands, CpG island shores and first exons is known to play a key role in th
59 on; survival was predicted for two different shores and four sampling times using a single recruitmen
64 B ALL subtypes, and methylation in CGIs, CGI shores, and in regions around the transcription start si
65 single-base resolution confirm that sloping shores are universal for hypomethylated CGIs in sperm an
67 treatment upgrades to the most affected near-shore areas, while simultaneously implementing legislati
73 enlisted men; 5.2% (21/406) of male marines shore-based in Okinawa, Japan; 2.7% (5/183) of female en
75 iology of "ice" bears in summer is unknown, "shore" bears purportedly minimize energy losses by enter
77 e to a redirection of production to the near-shore benthic zone, and large lakes may exhibit shifts i
78 king regions of active promoters, CpG island shores, binding sites of the transcription factor CTCF a
80 vious work has associated with distance from shore, but no genetic structure was associated with blea
81 showed that differential methylation of CGI shores, but not CGIs, significantly regulated Cav1 expre
82 ough December 2011 at the Mass General/North Shore Cancer Center, a community-based cancer center in
83 ight populations from the island and its off-shore cays, and applied the population genetics results
84 ression pattern of genes associated with CGI shore cDMRs was able to discriminate between disease phe
85 predator attack, foraging unusually close to shore, chemical or algal toxin exposure, abnormal weathe
86 ncipal investigators, and more companies off-shoring clinical trials, overcoming such barriers is of
87 ater, reduced subsurface oxygen both in near-shore coastal water and in the open ocean, rising coasta
88 ean 7.8-7.9, minimum 7.4-7.5), typical rocky shore communities with abundant calcareous organisms shi
89 d management solutions have focused on lower shore communities, neglecting the terrestrial-marine tra
94 ere, we removed sessile species from a rocky shore community in a way that deliberately mimicked natu
95 le outplants was reduced dramatically at mid shore compared to low shore levels regardless of the pCO
96 , a phenomenon that we described as "sloping shores." Computational analyses of human and mouse methy
97 cific and density-dependent effects of rocky shore consumers (crabs and snails) on community recovery
100 e fixed-effects summary odds ratio was 1.35 (Shore-corrected 95% confidence interval: 1.23 to 1.47),
101 eciprocity between epigenetic markers at CGI shores corresponding to differential gene expression in
105 re, we test the camouflage strategies of the shore crab (Carcinus maenas) in two habitats, being a sp
106 ze on a community comprised of the predator (shore crab Carcinus maenas), various grazing detritivore
107 oplastics may be ingested and inhaled by the shore crab Carcinus maenas, although the biological cons
111 ence of the minor form of CHH from the green shore crab, Carcinus maenas, was determined by automated
112 diments; marine invertebrates (snails, green shore crab, great spider crab, and edible crab); and tel
113 outhern New England (USA) the invasive Asian shore crab, Hemigrapsus sanguineus, preys on mussels (My
114 migrapsus takanoi, the Japanese brush-clawed shore crab, is a highly successful invader in European s
115 e to human antidepressant drugs; the striped shore crab, Pachygrapsus crassipes, was studied using an
118 compared to the physiological resilience of shore crabs in maintaining osmoregulatory and respirator
121 2015 field campaign generate large-scale on-shore currents that hit the coast, generating strong nar
124 high-dimensional methylation data sets (CpG Shore data, THREE data and NIH Roadmap Epigenomics data)
128 the highest activities associated with near-shore eddies and the Kuroshio Current acting as a southe
130 ethylation was overrepresented in CpG island shores, enriched within gene bodies but not in intergeni
134 lambeosaurines had less preference for near-shore environments than hadrosaurines in both Arctic and
135 the GOE there was pervasive suboxia in near-shore environments, allowing nonquantitative Se reductio
136 The global flux is dominated by shallow near-shore environments, where CH(4) released from the seaflo
139 dditionally, dynamic processes such as cross-shore equilibrium processes and alongshore sediment tran
140 ave evaluated the effects of the oil on near-shore estuarine fish species such as red drum (Sciaenops
141 Eleanor and Miles Harvard Medical School Shore Fellowship Grant, and Massachusetts General Hospit
142 nalysis were enriched in non-CpG islands and shores ([Formula: see text]) and depleted in promoter re
143 mass of aerosols arriving at North American shores from overseas is comparable with the total mass o
148 mulative ecosystem stress is highest in near-shore habitats, but also extends offshore in Lakes Erie,
149 ht environment resulting from differences in shore height and shading within the host macroalga, like
152 with Cav1 CGI shore methylation levels, with shore hypermethylation in minimally aggressive, luminal
153 aggressive, luminal breast cancer cells and shore hypomethylation in highly aggressive, basal-like c
154 all ponds, lakes, streams/rivers and the sea shore (i.e. downward QH), with Tw-Ta becoming increasing
156 waters also increased in abundances close to shore in southern California during the MHW, a pattern t
159 n of cytosine-phosphate-guanine (CpG) island shores in nine human iPS cell lines as compared to their
161 l colonization of subantarctic and Antarctic shores, in addition to recent genetic exchange among pop
165 g y(-1) (of mainly higher congeners) to near-shore Lake Ontario compared with volatilization of appro
167 tiple private and public values on its North Shore land holdings (Island of O'ahu) of approximately 1
170 onse, the morphotype associated with the low-shore-lengthened response times at high temperatures.
171 ion between the larval carry-over effect and shore level, suggesting little modulation of acidificati
172 ed dramatically at mid shore compared to low shore levels regardless of the pCO2 level that oysters e
173 gh juveniles grew less at mid shore than low shore levels, there was no evidence of an interaction be
174 ion of Infectious Disease Diagnostics, North Shore-LIJ Health System, and now is Vice President for G
175 ication of terrestrial, freshwater, and near-shore marine ecosystems, and comparable increases in pes
177 where DGT samplers were deployed in the near-shore marine environment of East Antarctica around the o
178 and contaminant monitoring in Antarctic near-shore marine environments need new techniques to overcom
180 particularly those associated with the lower shore, may exhibit less effective behavioural responses
181 nd Women's, Massachusetts General, and North Shore Medical Center) were evaluated for CMS reporting s
183 Recently, other patterns such as CpG island shore methylation and long partially hypomethylated doma
185 ncer aggressiveness associated with Cav1 CGI shore methylation levels, with shore hypermethylation in
188 rst study of Cav1 (a potential oncogene) CGI shore methylation, we suggest this phenomenon may repres
189 rst study of Cav1 (a potential oncogene) CGI shore methylation, we suggest this phenomenon may repres
191 eastern United States are most prevalent off-shore near the continental shelf-break but are also comm
193 present-day sea level along the southeastern shore of Bermuda contain remains of a former breeding co
196 ient particles collected on the southeastern shore of Lake Michigan during an event (July 6-8, 2015)
197 ranged from <DL to 2.6 ng/L on the southern shore of Lake Ontario near the mouth of the Oswego River
198 pitation samples were collected close to the shore of Lake Victoria at Entebbe, Uganda, between Octob
200 seawater of Kaneohe Bay on the northeastern shore of Oahu, Hawaii, by extinction culturing in seawat
206 e organisms of drift debris deposited on the shores of 30 remote islands from the Arctic to the Antar
207 m coastal climate of Gibraltar, close to the shores of Africa, raises hopes for the future recovery o
209 s of limpets, found attached to rocks on the shores of Cornwall, Wales and Scotland were explored for
210 a) and Brassica crop species, thrives on the shores of Lake Tuz, Turkey, where soils accumulate high
211 Tar balls collected from the Gulf of Mexico shores of Louisiana and Florida after the BP oil spill h
213 y urbanized estuary, and specifically on the shores of San Mateo County, the county most vulnerable t
214 amples were collected at five sites near the shores of the Great Lakes during the period 2008-2009, i
216 amples collected at five sites, all near the shores of the North American Great Lakes during 2008-200
217 protein 2 to the "cytosine-phosphate-guanine shores" of the Kcc2 promoter, and decrease in binding of
218 lted in a shift toward "reshoring" and "near-shoring" of mining processing capabilities as regional p
220 , but rather in the 3' UTR, gene bodies, CpG shores or 'offshore' sites, and both positive and negati
221 t enrichment of hypermethylated cDMRs in CGI shores (P < 10(-60)), non-CGI-associated promoters (P <
222 rpendicular erosion and 11 m for the maximum shore-perpendicular accretion during the study period.
224 we find upper limits of 25 m for the maximum shore-perpendicular erosion and 11 m for the maximum sho
225 n position of the 0.8-m contour sampled from shore-perpendicular profiles spaced at 20-m intervals al
226 ears of monthly profile surveys taken at two shore-perpendicular transects at Duck, North Carolina, U
227 ndomized, open-label, vision examiner-masked SHORE phase 4 study that compared monthly versus pro re
228 nic (10)Be concentrations across a sandstone shore platform in North Yorkshire, UK, to model the chan
229 nce decrease by 38-92% for a near-horizontal shore platform with a low-elevation cliff-platform junct
231 growth patterns in the western central near-shore portion of Second Connecticut Lake, Pittsburg, New
232 rths at U.S. ports that could be switched to shore power to yield the largest gains for society.
234 require many ships to be equipped to receive shore power, even if doing so would result in a private
236 thin promoter 'CpG islands' (CGIs) with 'CGI shores', recently described regions that flank CGIs with
237 ment development also now impacting the near-shore region of Lake Baikal, the resilience of the lake'
238 n due to hyper-methylation in the CpG island shore region of mmu-miR-15b in both the spermatozoa of F
239 osystems is more recent in oceanic than near shore regions, yet our understanding of human impacts on
244 wrinkles are preserved in barely bioturbated shore-shallow lacustrine siliciclastic deposits of the L
248 trification, particularly involving electric shore-side vehicles (ESVs), has a significant impact on
249 dulating coseismic subsidence patterns, near-shore slip velocities, and the seismic and tsunami hazar
251 nced clones revealed that G. duebeni, a high-shore species with the highest thermal tolerance, expres
252 Tigriopus californicus, which inhabits rocky-shore splashpools where diel fluctuations of temperature
258 compare ecological shifts in subtidal rocky shore systems along CO2 gradients created by volcanic se
263 carried out in the late 1990s of open rocky shores that are common along the northern part of the 70
266 occurs outside of CpG islands and CpG island shores, thus rejecting the hypothesis that the increase
267 ic deep-sea brine pool sited close enough to shore to chronicle floods, yet be otherwise undisturbed
269 case study of one measurement drive from the shore to the precoastal mountain range furthest downwind
270 cal study was carried out in Rumonge, a lake-shore town where 318 people were admitted to hospital wi
271 ) Recession due to sea level rise, (3) Cross-shore transport due to waves, and (4) Residual processes
272 , wave-driven processes (longshore and cross-shore transport) still account for 34% of shoreline chan
275 tance Laboratory Network (AR Lab Network) to shore up the national capacity for detecting several res
276 fic work has proceeded in a robust manner to shore up the validity of APS as a diagnostic construct.
279 onger increase in peak- and late-season near-shore upwelling in the northern limb of the California C
281 tach themselves to rocks near tide-swept sea shores using byssal threads formed from their extracellu
282 ng along with repeat testing after return to shore was available for 120 of the 122 persons on board
284 1.8 +/- 2.7 Tg, is consumed annually in near-shore waters (<50 m), suggesting that aerobic methanotro
286 d the topshell Gibbula) from a coastal rocky shore, we found that the capacity to predict the combine
288 t geographic region, depth, and proximity to shore were significant predictors of community structure
289 Gene bodies, intergenic regions, and CpG shores were preferentially demethylated during erythropo
293 pment of oscillatory biological reactions at shores where waves impinge on rocks and bring nutrients
295 s significantly enriched in CpG island (CGI) shores while depleted in CGIs themselves, especially in
296 te concentrations yield maximal biomass near shore, while offshore biomass is positively correlated w
297 combined cycle (without CO2 capture) and on-shore wind power plants, both from a levelized and margi
299 g to show that subsea permafrost in the near-shore zone of the ESAS has a downward movement of the ic