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1 atures, and the conversion of forest to peri-urban.
3 w of all massive transfusions provided in an urban academic hospital from January 1, 2009, through De
9 randomized clinical trial was conducted at 5 urban addiction clinics in Norway between November 1, 20
10 /ethnicity, probation time, and offense at 2 urban agencies that exemplify specialty and traditional
11 onsiders ENM releases to compartments (e.g., urban, agriculture) in a manner that reflects their diff
14 st mechanistic insights into how exposure to urban air pollution leads to activation of guinea pig an
15 provides an overview of cigarette smoke and urban air pollution, considering how their composition a
21 ncluded N-rich DOM sources characteristic of urban and agricultural development, including chicken an
22 rticularly relevant in watersheds undergoing urban and agricultural development, leading to increased
23 ndancy analyses revealed that in the summer, urban and agricultural streams were abundant in chloroph
25 les/mile) were larger than those measured on urban and drayage routes (i.e., 5.06 x 10(11) to 1.31 x
27 indoor and outdoor averages, via archetypal urban and indoor settings, to 3646 real-world cities in
28 ive spatial autocorrelation was recorded for urban and nonurban ponds at 0-50 km (distance between po
29 gh July 31, 2015, from government schools in urban and periurban areas surrounding Bangalore, India.
30 es is affected by the confluence of polluted urban and relatively clean marine airmasses, each with d
32 ng medical care and patient outcomes between urban and rural areas in China during this period are no
34 g system replacement, while also considering urban and rural disparities and spatial colocation of nu
35 ment was not significantly different between urban and rural hospitals in any study year, with an adj
37 ifying exposure from indoor and ground-level urban and rural outdoor sources using an effective indoo
38 ex, socioeconomic position, causes of death, urban and rural residence, and preexisting comorbidities
40 Results were generally consistent between urban and suburban/rural census block groups, and for da
42 es, forests that have been converted to peri-urban, and increased precipitation during spring migrati
43 e carbon and nitrogen dynamics indicated the urban aquifer also serves as a biogeochemical reactor.
51 nization have led to higher levels of BTs in urban areas and provide a glimpse into future BT dynamic
53 e average mid-sleep time of people living in urban areas depends on the age and gender of each cohort
54 On the one hand, we found that lizards from urban areas differ from nearby forest lizards in that th
55 ected associations with shorter distances to urban areas during migration, and stronger than expected
56 ng the boundaries and within the interior of urban areas during migration, especially in the autumn w
57 bird populations are more likely to occur in urban areas during migration, especially in the autumn.
59 antial capital and labor flows from rural to urban areas even though these differ only in the underly
60 erifolia tree leaves has been sampled in the urban areas of 28 European cities, over 20 countries, wi
63 ss primary production (GPP) of vegetation in urban areas plays an important role in the study of urba
64 y cycle (changes in vegetation greenness) in urban areas starts earlier (start of season, SOS) and en
65 s and human exposure to nanosized aerosol in urban areas, and potentially may act as nanosized conden
66 itated the success of some native species in urban areas, but it has also allowed human pests and dis
67 relationships between residence in poor and urban areas, race/ethnicity, and asthma morbidity among
84 ing investment (clutch size), indicated that urban birds generally have higher survival, but smaller
85 example, estimated nighttime noise levels in urban block groups with 75% vs. 0% black residents were
86 ngs provide strong integrative evidence that urban blue tit nestlings are not receiving a suitable di
87 ion adult (aged >/=19 years), non-immigrant, urban Canadians in 30 cities who responded to the mandat
88 lasma pneumoniae in Thailand have focused on urban centers and have not included molecular characteri
91 urces of atmospheric pollution identified in urban centers is derived from both industrial and motor
92 frican migrants in Europe and nonmigrants in urban centers will inform and support targeted health ca
99 s study is that it was conducted at a single urban clinic, and the generalizability to other settings
101 he year, with increased travel from rural to urban communities after national holidays, for example.
105 ved in the least-urban counties; in the most-urban counties, a 1.13% (0.73%, 1.54%) increase was obse
106 Restrictions were only implemented in highly urban counties, based on US Department of Agriculture Ec
107 increase in PM2.5, was observed in the least-urban counties; in the most-urban counties, a 1.13% (0.7
114 neighborhood physical disorder-a measure of urban deterioration-is thought to encourage crime and hi
115 are correlated with their putative stage of urban development as measured by a series of socio-econo
116 to be an unparalleled proxy for tracking the urban development of ancient Rome over more than a mille
117 presents evidence on the mechanisms linking urban development patterns to rapid evolutionary changes
118 tors, suggesting a strong connection between urban development, increasing physical connectivity, and
120 ssed exposure to violence through either the urban district-level homicide rate or self-reported meas
121 assess the relative impact of five types of urban disturbances including habitat modifications, biot
125 Randomized clinical trial conducted at 2 urban EDs in the Bronx, New York, that included 416 pati
126 f Care for patients identified with HCV in 2 urban EDs, and consider the results in the context of ou
129 ppreciably until several kilometers into the urban environment, where concentrations of solutes such
131 ether, our results suggest that selection in urban environments favors different traits than selectio
133 UHI) is a widely observed phenomenon whereby urban environments have higher temperatures and differen
134 ortant sources of fine particle pollution in urban environments, but their contribution to the atmosp
136 tic habitats (reduced taxonomic richness) in urban environments; in contrast, they support high taxon
141 include mining infrastructure establishment, urban expansion to support a growing workforce, and deve
142 derstanding of how global patterns of future urban expansion will affect the world's cultivated areas
145 emissions, land occupation, water use, etc.) Urban farming (UF) has been advocated as a means to incr
146 we developed a novel method to estimate sub-urban, food-borne carbon and land footprints using multi
147 oxide (NO2) to explore relationships between urban form and air pollution for a global data set of 12
149 the need for future study of how changes in urban form and related land use and transportation polic
151 cle facilities) was transformed to match the urban form of Indio - Cathedral City, California, United
152 We also find that the combined effect of urban form on NO2 is larger for small cities (beta x IQR
153 (a city at the 75th percentile for all three urban-form metrics, and with a network of buses, trams,
154 among Ghanaian adults residing in rural and urban Ghana and 3 European cities (Amsterdam, Berlin, an
155 naian men was 34.7% in rural Ghana, 45.4% in urban Ghana, 53.9% in Amsterdam, 61.0% in Berlin, and 52
157 rtance of maintaining a diverse portfolio of urban green spaces and plant communities therein to faci
160 ing use of this technology, here we evaluate urban greenspace 3D connectivity, taking into account th
173 sures, including allergens and endotoxin, in urban homes stimulate the development of cytokine respon
176 significant for rural households but not for urban households, suggesting differing dependence on wat
178 ping new hypotheses concerning adaptation to urban infrastructure and human socioeconomic activity.
182 d from unsustainable defense of the wildland-urban interface to developing fire-adapted communities.
184 PE atmospheric concentrations across a large urban landscape and specific knowledge gaps at the inter
186 Transition of populations from rural to urban living causes landscape changes and alters the fun
187 history of allergy, OR 2.1 (95% CI 1.6-2.8), urban living, OR 1.9 (95% CI 1.2-2.9), and male sex, OR
188 ctivity in two neighbouring communities, one urban (Milange) and one rural (Tengua), in a region of M
189 utional cynicism, and segregated patterns of urban mobility and organizational ties that differential
191 od lead levels (BLL) were investigated in an urban neighborhood in Philadelphia, PA, with a history o
192 of park users and their physical activity in urban neighborhood parks with and without walking loops.
193 uropean starlings (Sturnus vulgaris) cohabit urban neighborhoods and may serve as sentinels for these
194 statistically significant relationship with urban NO2; their combined effect could be substantial.
197 tatus, household sanitation and hygiene, and urban or rural residence) in nonpregnant WRA.Cross-secti
198 able models that were adjusted for age, sex, urban or rural residence, and socioeconomic status, elev
199 tential, however, requires understanding how urban parameters affect the fraction of individual trips
200 we compared soil microbial communities in 41 urban parks of (i) divergent plant functional types (eve
201 ts: both bacterial and fungal communities in urban parks responded to plant functional groups, but fu
202 less diverse soil microbial communities than urban parks that are under continuous anthropogenic dist
203 icate that, despite frequent disturbances in urban parks, urban soil microbes still followed the clas
205 ications for global public health policy and urban planning and highlight the role of activity inequa
206 tion is a pressing problem for sociology and urban planning, but existing methods have limitations.
207 the examples of better rain-data management, urban pluvial flood-risk management and forecasting, dri
214 ation after recall from screening in a large urban population after implementation of digital breast
215 than 500000 people contain a majority of the urban population and are where much of the future urban
217 ion sites, would reduce the vulnerability of urban populations and infrastructure to temperature extr
218 this may be an important limiting factor for urban populations of this and potentially many other spe
222 tantially affected attendance patterns, with urban practices in affluent areas that typically have ap
224 ween Oct 1, 2014, and April 30, 2016, at the urban Rahima Moosa Mother and Child Hospital (RMMCH), Jo
227 l mortality did not differ between rural and urban regions (1.44% vs 0.89%; P = .09); however, 89.6%
229 the trauma care in Lima, Peru, and included urban resident and faculty surgery and trauma care physi
230 ort a higher PSQI score (4.45 +/- 2.81) than urban residents did (4.18 +/- 2.60) (p < 0.001) and the
231 nsitivity analyses and seemed stronger among urban residents, especially those who lived in major cit
232 ious driving cycles: Artemis driving cycles (urban, road, and motorway), the New European Driving Cyc
233 solar photovoltaic (PV) system deployment on urban rooftops to reduce the UHI, and we price one poten
235 full range of potential impacts of trees on urban runoff, which includes deposition of nutrient-rich
237 did a prospective cohort study (Prospective Urban Rural Epidemiology [PURE] in 135 335 individuals a
238 intense during the summer and at night, with urban-rural aerosol pH differences in excess of 0.8 and
244 cribed dermatologic medications at a single, urban, safety-net hospital outpatient dermatology clinic
246 s the sensitivity of Austrochiltonia spp. to urban sediment contamination and identifies bifenthrin a
247 ed insights in the structure and dynamics of urban segregation that would be otherwise easy to miss o
248 .49; 95% CI, 1.30-1.70), and treatment in an urban setting (HR, 1.45; 95% CI, 1.21-1.73.) Although so
249 ology of first-episode psychoses in rural or urban settings since the introduction of early intervent
250 two-thirds of the studies were performed in urban settings with predominantly African-American women
251 n the extinction of native remnant plants in urban settings, or whether they could have other effects
254 he issues involved in testing and validating urban simulation models involving spatial data and its a
255 Ten ambient PM samples collected from an urban site were analyzed, and although DTT oxidation was
258 espite frequent disturbances in urban parks, urban soil microbes still followed the classic patterns
260 These findings support the conclusion that urban sources of ALAN can broadly effect migratory behav
261 t baboons are at risk of being herded out of urban spaces that contain high-energy anthropogenic food
263 he exposure to Campylobacter when harvesting urban stormwater for toilet flushing and irrigation acti
264 ment, or LID) has the potential to transform urban stormwater runoff from an environmental threat to
265 ating the movements of people and resources, urban street networks offer a spatial footprint of these
266 ple, we estimated high average COI in a peri-urban subregion with lower transmission intensity, sugge
267 emissions of volatile organic compounds from urban/suburban vegetation and corresponding ground-level
268 F) has been advocated as a means to increase urban sustainability by reducing food-related transport
269 consistently extract the main skeleton of an urban system and to further classify each road in terms
276 of mosquitoes and is capable of an epidemic, urban transmission cycle with high rates of infection.
278 nts with 1 or more previous admissions to an urban trauma center (recidivists) were identified and co
279 delivery of dsRNA to an invasive forest and urban tree pest, the emerald ash borer (EAB, Agrilus pla
282 ing econometrics to quantify a key source of urban ultrafine particles.The biofuel ethanol has been i
285 omly varying blocks, stratified by location (urban vs rural) and size of rings (</=20 individuals vs
286 andom sampling (according to age, residence [urban vs rural], and sex) in all countries to recruit el
287 tern, central, and eastern China], urbanity [urban vs rural], ethnic origin [Han and non-Han], occupa
288 rated since 1985, sex, socioeconomic status, urban (vs rural) residence, and causes of death were sim
289 mple of 17633 patients (1438 rural and 16195 urban) was created to track hospital outcomes (78.9% wit
295 ons and sources of annual N and P loads from urban watersheds are poorly characterized in northern ci
297 ss attributed to surface water recreation at urban waterways, lakes, and coastal marine beaches is re
299 search identifies contaminants of concern in urban wetland sediments by assessing sediment toxicity u
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