ライフサイエンスコーパス: residential

1 adverse effects on a range of commercial and residential activities.

2 lated patient calls to a random sample of US residential addiction treatment facilities to investigat

3 Using the residential address at age 6 years produced similar resu

4 es in the 250 m and 1250 m radius around the residential address for each individual included in the

5 PM2.5 concentration at the residential address of each participant was estimated ba

6 luding 5,373 subjects without information on residential address or relevant covariates, we included

7 ency's (EPA's) Air Quality System matched to residential address, in 1,446 mother-infant pairs who we

8 was assigned to case and control days at the residential address, using weather stations within 15 km

9 ta on environments around each participant's residential address, we examined whether density of phys

10 lution Effects project, at the participants' residential address.

11 with a 1 km buffer around each participant's residential address.

12 e associated with asthma symptoms beyond the residential address.

13 years after the disaster, we ascertained the residential addresses and health status of 3,594 survivo

14 Residential addresses from 1987 to 2016 were obtained fr

15 Catchment areas were based on residential addresses of enteric fever patients using st

16 tation Index (NDVI) using 500 m radii around residential addresses to measure greenness, and the Mini

17 after ambient PM2.5 exposures, estimated at residential addresses using a spatiotemporal model.

18 rom the hospital population health database, residential addresses were geocoded and linked to their

19 ed on nitrogen oxides (NOx) at participants' residential addresses.

20 use regression at the participants' geocoded residential addresses.

21 ces when using workplace in combination with residential addresses.

22 ities in 100- to 400-m radius buffers around residential addresses.

23 ly on exposure estimates based on linkage to residential addresses.

24 Patients were assigned exposures based on residential addresses.

25 l grid data on neighborhood disadvantage via residential addresses.

26 where a monetary variable is provided to the residential agents (sampled from reported income data),

27 opy of its states as the aggregate number of residential agents surrounded by a threshold of equally

28 er controlled laboratory conditions and also residential air and ambient outdoor air in Baltimore, MD

29 47.1%] were men), 5780 were assigned outdoor residential air pollution concentrations in the year of

30 investigated whether early-life exposure to residential air pollution was associated with leukocyte

31 isms and regulatory T cells but dependent on residential alveolar macrophages (AMs).

32 test the spatial proxies used in estimating residential and commercial building emissions.

33 Differences in the subcounty residential and commercial building sectors are driven b

34 enges is to improve the energy efficiency of residential and commercial buildings, which cumulatively

35 inear mixed models, we found that increasing residential and energy development within deer habitat w

36 We examined the effect of restoration of residential and housing-related financial resources on r

37 he area emissions were likely primarily from residential and industrial wood combustion.

38 xpression of preferences is unconstrained by residential and lineage norms, and is detectable even wh

39 tion is mainly determined by the movement of residential and migratory avian populations.

40 light diffusers and smart windows, both for residential and mobile use.

41 construction materials stocked in buildings (residential and nonresidential), roads, and pipe network

42 Intake fractions from residential and occupational indoor sources range from 4

43 ve been used to teach DVL to more than 8,500 residential and online students, and results from this e

44 increased after bystander defibrillation in residential and public locations.

45 Less is known about the combined impact of residential and school exposures on pediatric asthma.

46 use spatial analysis methodology to analyze residential and school proximity to major roadways and p

47 trongly associated with the outcome when the residential and work/study environments were entered in

48 y of site had a unique spatial distribution; residential and workplace address were visually and stat

49 lection but could select between mock cases' residential and workplace addresses to localize the sour

50 oximately 6.0%, 7.7%, and 4.2% in the power, residential, and industrial sectors, respectively, under

51 h GHG emissions from coal used in the power, residential, and industrial sectors.

52 NG is a common fuel for residential appliances because of low cost, high energy

53 per phase at a large 22-well pad sited in a residential area of Weld County, Colorado.

54 ere consistent across subgroups of age, sex, residential area, and comorbidities.

55 investigated in an agriculturally dominated residential area, showing that an increase in adverse bi

56 UFPs adversely affect air quality over large residential areas downwind of airports, but their reprod

57 6-2017 and 2017-2018, stormwater runoff from residential areas was monitored in paired cities to dete

58 Living in high-density residential areas with richness of facilities and densit

59 rborne livestock-related microbial levels in residential areas.

60 children and adults in tropical or deprived residential areas.

61 ng conducted on multiwell pads (MWPs) and in residential areas.

62 mmon and may affect large, densely populated residential areas.

63 We calculated each participant's residential-based distance to a major roadway and used a

64 PreFAAs were measured in matching samples of residential bedroom air collected by passive sampler and

65 d with medium-term to chronic (1 mo or more) residential black carbon +5.33 x 10(5) particles/ml high

66 Children's residential black carbon concentrations were estimated b

67 r an interquartile range increment in annual residential black carbon exposure.

68 sectional study investigates associations of residential building characteristics and markers of neig

69 sumption and emissions (2020-2050) for seven residential building types representative of California

70 consumption which differs by +1% to -15% for residential buildings and by -4% to -21% for commercial

71 Urban residential buildings make large contributions to energy

72 er than current assumptions imply, while for residential buildings occupancy rates vary widely by nei

73 onsumption per square meter in China's urban residential buildings occurred in 2012 when accounting f

74 y used to measure energy efficiency in urban residential buildings.

75 n Batek hunter-gatherers (n = 93 d across 11 residential camps) living in the tropical rainforests of

76 cipients and subsidising the construction of residential care beds and operating costs.

77 stem is characterised by rapid growth of the residential care sector, slow development of home and co

78 shorter lifespan, and increased admission to residential care than patients with Alzheimer's disease.

79 se of urinary catheter and longer latency to residential care than progressive supranuclear palsy pat

80 ech, cognitive impairment, severe dysphagia, residential care).

81 y sensed colour infrared data within a 500 m residential catchment, and an urbanicity index derived f

82 rticulate matter and nitrogen dioxide at the residential census-tract level.

83 However, the relevance of individual residential changes and their importance among specific

84 ting that the decrease of entropy due to the residential clustering has a parallel and independent ef

85 Nur-Sultan in 2012 that could be due to the residential coal combustion and vehicle exhaust under po

86 Source testing on Chinese residential coal combustion provides direct evidence tha

87 nces between Taiwan and other countries, but residential colleges and universities present similar ch

88 less in diameter) emissions from commercial/residential combustion and smaller reductions in nonroad

89 oxide (PBO) is a pesticide synergist used in residential, commercial, and agricultural settings.

90 tainers found along a canal that divided two residential communities in Donna, Texas, USA.

91 and processing impose public health risks on residential communities through air and water pollution.

92 o increase adaptation by some ecosystems and residential communities to more frequent fire; (iii) act

93 romotes adaptive responses by ecosystems and residential communities to more warming and wildfire.

94 laza and consisting of both governmental and residential components.

95 inal costs that code requirements add to new residential construction, the quantity of carbon emissio

96 at the developmental processes through which residential contexts promote upward mobility begin early

97 Case-residential data were geocoded, linked to census tract p

98 Case residential data were geocoded, linked to census tract p

99 We examined the association of obesity with residential density in a large and diverse population sa

100 design can include mixed land use, increased residential density, proximity to community or neighborh

101 The state has identified residential designs that "bring value to the grid" as a

102 lts underscore the significance of expanding residential development on mule deer populations, a fact

103 erities; and (iv) incentivizing and planning residential development to withstand inevitable wildfire

104 Each doubling in residential distance to nearest major road during childh

105 deled contribution to BLLs from ingestion of residential drinking water ranged from ~10 to 80%, with

106 s, we see that perfluoroalkyl acid levels in residential dust appear to decrease over time, particula

107 t samples, in 32 Canadian and United States' residential dust samples, and in 10 sediment samples col

108 rations of these compounds than the Canadian residential dust, while intermediate levels were detecte

109 te levels were detected in the United States residential dust.

110 cal relationship between physical hazard and residential economic impact at a community level for the

111 jections of the climate-sensitive portion of residential electricity demand are based on estimating t

112 Rural residential emissions affect not only rural but urban ai

113 n of their total impacts, whereas commercial/residential emissions have the smallest.

114 itatively evaluate the contribution of rural residential emissions to PM(2.5) (particulate matter wit

115 ns: Coexposure to elevated concentrations of residential endotoxin and ambient PM(2.5) in all partici

116 three scenarios witness a dramatic growth of residential energy consumption and a steady increase of

117 Rural residential energy consumption in China is experiencing

118 olicy tools, as well as the ongoing trend of residential energy consumption in China.

119 on sources, to offset projected increases in residential energy demand.

120 Residential energy use accounts for roughly 20% of green

121 We calibrate residential energy use against metered data, accounting

122 Although residential environment might be an important predictor

123 Although residential environment might be an important predictor

124 e to a university classroom and 3x less than residential environments.

125 ated spatiotemporal models to estimate daily residential exposure to [Formula: see text], [Formula: s

126 Multiple approaches were used to assign residential exposure to factors of the built environment

127 cative interaction between long-term ambient residential exposure to fine particulate matter < 2.5 mi

128 We estimated residential exposure to green spaces using satellite-der

129 Residential exposure to livestock-related bacteria and A

130 ighborhood scale to more accurately estimate residential exposures.

131 ool Children (BREATHE) Project, we estimated residential [Formula: see text] exposures by land use re

132 ssions, primarily from vehicle emissions and residential fuel burning.

133 We show that residential gardens and allotments (community gardens) a

134 industry dedicated to feeding wild birds in residential gardens.

135 rt study to examine the associations between residential green spaces and the incidence of acute myoc

136 an age difference; the protective effect of residential greenness (the highest vs. lowest quartile)

137 ~ 53% of the protective association between residential greenness and cardiovascular mortality.

138 ive of this study was to examine surrounding residential greenness and depression risk prospectively

139 We assessed the association between residential greenness and mortality in an older cohort i

140 ases in AMI and HF incidence associated with residential greenness explained ~ 53% of the protective

141 We also assessed modifying effects of residential greenness levels (derived from satellite ima

142 -environment interaction mechanisms in which residential greenness may benefit health.

143 cent evidence suggests that higher levels of residential greenness may contribute to better mental he

144 Exposure to high residential greenness modified the association at 18 yea

145 We tested whether the protective effects of residential greenness on cognitive function differ by AP

146 The protective effects of residential greenness on cognitive function differed by

147 Each interquartile range increase in residential greenness was associated with a 7% [95% conf

148 Residential greenness was linked to a ~ 10% decrease in

149 Residential greenness was measured using the satellite-b

150 Conversely, residential greenness was not associated with any delay

151 1-1.08 per interquartile increment), whereas residential greenness was protective, being associated w

152 Built environment metrics of residential greenness were modelled in terms of normalis

153 ed models, living in the highest quintile of residential greenness within [Formula: see text] was ass

154 Analyses controlled for residential greenspace and other neighbourhood and indiv

155 on emissions from power generation and rural residential heating sectors.

156 electricity for in-home combustion for rural residential heating.

157 Based on residential histories and environmental data on air moni

158 Residential history and main water source used for the f

159 te operation of appliances, we estimate that residential homes and appliances could release 9.1 Gg CH

160 uction under NSF/ANSI Standards 53 and 42 to residential homes in that zone.

161 frequently used by residents in care homes (residential homes or nursing homes that provide resident

162 tions is estimated in terms of the aggregate residential homogeneity and the aggregate income homogen

163 Residential housing had two times the magnitude of effec

164 ight intensity (ANLI) and average commercial residential housing price (ACRHP) adjusted by annual inf

165 he electrical grid is decarbonized, then the residential housing sector can meet the 28% emission red

166 inal activity (OR, 5.89; 95% CI, 4.38-7.92), residential independence (OR, 3.41; 95% CI, 2.57-4.52),

167 The median PFOA intakes from residential indoor air (5.7 pg kg bw(-1) day(-1)) and pe

168 This study examined residential indoor air in homes (n = 99) in southeast Lo

169 Further study of residential indoor air in low-income women's homes in th

170 nd 2.3 pg kg bw(-1) day(-1) were obtained in residential indoor air, while 1.0, 0.10, 3.3, 0.33, 0.88

171 50% lower than the median concentrations in residential indoor air.

172 f which can be found in indoor air including residential indoor air.

173 t phthalates and adipates) were installed in residential indoor environments.

174 We observed substantial variations in 23 residential indoor WSOG concentrations measured in real

175 To account for socioeconomic factors such as residential instability and material deprivation, we als

176 ersely affect child development, but whether residential interventions and dust removal can prevent c

177 While residential irrigation facilitates persistence of mosqui

178 Counseling and nutritional interventions or residential lead hazard control techniques did not reduc

179 We quantified the influence of a residential lead hazard intervention and dust control on

180 to receive an intervention to reduce either residential lead or injury hazards before delivery.

181 We estimated annual average ambient residential levels of particulate matter < 2.5 mum and <

182 We investigated associations between residential location and ASD in the children of Nurses'

183 We explored relationships between ASD and residential location both at birth and at age 6 years (i

184 nd a control group matched for age, sex, and residential location from households of the general popu

185 bsequent survival according to a public or a residential location of the cardiac arrest after nationw

186 ing conceptualizations of community based on residential location or resource use are limited with re

187 ambient PM(2.5) exposure at a participant's residential location was associated with higher odds of

188 nancy using a geographic information system, residential location, and California's comprehensive agr

189 nonphysicians (n = 45,736) on age, sex, and residential location.

190 00 and 1,000 m surrounding the participants' residential locations at each follow-up.

191 differences in asthma onset, smoking status, residential locations, percentage of blood and/or sputum

192 n dioxide (NO(2)) exposures at participants' residential locations.

193 bystander defibrillation remained limited in residential locations.

194 ophages, T cells, dendritic cells (DCs), and residential macrophages near high endothelial venules, t

195 The residential mobility patterns of modern hunter-gatherers

196 ue theorem in the context of hunter-gatherer residential mobility using historical foraging data from

197 l, nuclear households, weak family ties, and residential mobility, fostered greater individualism, le

198 y strategies and the Epigravettians applying residential mobility.

199 were developed to evaluate alternatives for residential municipal SWM, which included combinations o

200 ually and statistically clustered around the residential neighborhood and city center sites respectiv

201 socioeconomic circumstances in participants' residential neighborhoods, categorized as high versus lo

202 ity, or language, which suggests that ethnic residential networks transmit information about employme

203 uring methane concentrations in exhaust from residential NG appliances was conducted in Boston and In

204 methane emissions can be attributed to U.S. residential NG appliances, corresponding to ~830 [530-45

205 Residential normalized difference vegetation index (NDVI

206 ecords from 2008-2013 and estimated maternal residential O3 concentrations from conception until deli

207 n blocks of two, stratified by type of home (residential or nursing).

208 We examined the association between residential outdoor LAN and breast cancer incidence usin

209 e modeled by land use regression: individual residential outdoor levels of particulate matter with ae

210 nisms, our findings suggest that exposure to residential outdoor light at night may contribute to inv

211 re length (aTL) and estimated annual average residential ozone (O(3)) and fine particulate matter wit

212 oring to capture changes in agricultural and residential pesticide use over time.

213 We did a residential plot-randomised controlled trial in a peri-u

214 ent associations of 24-months moving average residential PM2.5 exposure and physical activity updated

215 We estimated daily residential PM2.5 using satellite data in combination wi

216 between postbronchodilator FEV(1) and annual residential pollutant attributions.

217 est health insurer covering 15% of the Swiss residential population.

218 gal-sIgE positivity was 2.48 compared to the residential population.

219 use regression model based on each subject's residential postal code.

220 Based on annual residential postal codes, we assigned 5-y running averag

221 s proximity to major roadways based on their residential postal-code address in 1996, 5 years before

222 sadvantage system, a score allocated to each residential postcode based on factors like income, educa

223 Detection in orchards and residential properties was real time, ~2 s per tree.

224 ied potential relationships between maternal residential proximity to agricultural use of neurotoxic

225 A, b) receiving Flint water at home, and c) residential proximity to cooling towers; however, for 20

226 We evaluated associations between residential proximity to elemental sulfur applications a

227 tudies showing health effects in relation to residential proximity to farms.

228 We investigated whether residential proximity to flaring from OGD was associated

229 imed to investigate the relationship between residential proximity to OGD and birth outcomes in Calif

230 We estimated associations of residential proximity to OP use during pregnancy with co

231 Owners' Loan Corporation (HOLC) nationalized residential racial segregation via "redlining," whereby

232 These results suggest an association between residential radon and brain cancer mortality.

233 e observed a significant correlation between residential radon with brain cancer mortality for males

234 deprivation, rural or urban settlement, and residential region.

235 estion, we leveraged a natural experiment of residential relocation in the aftermath of the 2011 Japa

236 l disasters are often associated with forced residential relocation, thereby affected people experien

237 Residential remoteness was associated with coronary arte

238 We aimed to investigate whether residential road traffic noise increases the risk for hy

239 of brining as a BMP for salt application on residential roads would result in a decrease in chloride

240 cleaning in a chamber designed to simulate a residential room.

241 The persisting residential rules and even a direct kinship relation acr

242 n Health Administration transplant programs, residential rurality status does not portend longer wait

243 zard of transplant among veterans differs by residential rurality.

244 reaching corresponding regulation levels for residential scenario after rational treatment time (from

245 oor air levels were higher than those in the residential scenario.

246 uce electric energy consumption (EEC) in the residential sector and simultaneously achieve a more des

247 he appliances and buildings that make up the residential sector could contribute significantly to nat

248 s represent the first-best policy option for residential sector GHG abatement in California.

249 ure mortality associated with the commercial/residential sector was twice that associated with power

250 te cobenefits, particularly when used in the residential sector, with proper methane leakage control.

251 biofuel were replaced by natural gas in the residential sector.

252 ciency has been rising in the industrial and residential sectors but only recently in the health care

253 transportation, industrial, commercial, and residential sectors).

254 icies in the power generation, industry, and residential sectors.

255 occupational structure affect socio-economic residential segregation in global cities.

256 nomic status and structural factors, such as residential segregation, come into play in determining H

257 , 20-49-year-olds, racial/ethnic minorities, residential segregation, income inequality, uninsured, d

258 research to link racist practices, including residential segregation, to the heterogeneous patterns o

259 ime neighborhood measures and sensitivity to residential self-selection.

260 uch as appliance age and usage, climate, and residential setting could influence the emissions profil

261 s that are commonly used in agricultural and residential settings with adverse respiratory effects.

262 iest evidence of a prehistoric high-altitude residential site.

263 ements were performed in 2014 and 2015 at 61 residential sites in The Netherlands.

264 also report a relatively low RBA (23%) in a residential soil where the major Pb species was found to

265 measurements for a subset of house dust and residential soils collected in the AHHS, with the primar

266 Applying the model to residential solar customers in Germany, we find that beh

267 f ca. 900 to 1200 CE consists of at least 37 residential spaces enclosed by ridges of oyster shell up

268 he bead making of persons distributed across residential spaces with unprecedented resolution.

269 Test excavations in 10 of these residential spaces yielded abundant evidence for the pro

270 tracts (family income, poverty, deprivation, residential stability, and percent white, black, or fore

271 Yunnan to investigate screening and regional residential status as predictive factors.

272 In patients diagnosed not by screening, XF residential status was a significant predictor of improv

273 factors that underlay the association of XF residential status with improved OS in patients diagnose

274 ged intensive care with respect to survival, residential status, functional recovery, and quality of

275 follow-up, hospital and long-term survival, residential status, patient-centered outcome measure use

276 sidue, wood, and solid waste combustion in a residential stove were analyzed using transmission elect

277 osure, progestogen users had lower levels of residential sun exposure and were more likely to report

278 We generated trajectories of change in residential surrounding built-up land use (buffer areas)

279 evaluated the association between changes in residential surrounding built-up land use and cardiometa

280 t observe any consistent association between residential surrounding greenspace and arterial stiffnes

281 gnificant associations were observed between residential surrounding greenspace and baseline or 4-y p

282 Residential surrounding greenspace was characterized usi

283 reducing opioid withdrawal symptoms during a residential tapering program.

284 inear exposure-response function for average residential THM levels and bladder cancer by pooling dat

285 We determined the impact of residential traffic on mortality during treatment of act

286 We found a positive association between residential transportation noise and diabetes, adding to

287 ease, we examined the influence of long-term residential transportation noise exposure and traffic-re

288 t individuals scanned at the end of a 30-day residential treatment programme.

289 reasingly used to treat polyurethane foam in residential upholstered furniture.

290 sex, monthly income, geographic location and residential urbanization level, hyperlipidemia, diabetes

291 f agricultural drift, para-occupational, and residential use exposure pathways to house dust pesticid

292 For the residential use pathway, GMs were 1.3 (95% CI: 1.1, 1.4)

293 o of GMs from two groups (para-occupational, residential use).

294 g agricultural drift, para-occupational, and residential use.

295 ated to crops (pesticides and nutrients) and residential uses (pyrethroids) were found to be more str

296 n some age groups, under realistic local and residential water use conditions, drinking water can be

297 les Basin, we examined the effect of outdoor residential water use restrictions on the abundance of t

298 state government put restrictions on outdoor residential water use, including landscape irrigation, d

299 and P, we monitored stormwater outflow in a residential watershed in Saint Paul, Minnesota during 20

300 Within their residential zip code, patients had a median of 25 "less-