ライフサイエンスコーパス: residential

1 or healthcare utilization data, and used the residential address as the primary location for exposure

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

3 al's exposure to PM2.5 and NO2 outside their residential address is highly correlated (Pearson's R of

4 et network buffers around each participant's residential address with geographic information systems.

5 Londoners LHEM exposure with exposure at the residential address, a commonly used exposure metric in

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

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

8 for PM2.5 and 63% lower for NO2 than at the residential address.

9 e associated with asthma symptoms beyond the residential address.

10 in highly correlated predictions at external residential addresses (R(2) of 0.89 for UFP and 0.88 for

11 correlated with social insecurity, in which residential addresses and contact information change fre

12 ighborhood disadvantage grid with the use of residential addresses between the years 2000 and 2008 an

13 dioxide; NO2) from a dispersion model, using residential addresses from 1971 to the date of diagnosis

14 nd stationary monitoring LUR models at 12682 residential addresses in Amsterdam.

15 ide (NO2) exposure was estimated for current residential addresses using a validated land-use regress

16 00 cases reported during 1995-2011 and their residential addresses were analysed for spatial risk and

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

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

19 -balance PM2.5 infiltration model to predict residential AER (Tier 1), infiltration factors (Tier 2),

20 California, we statistically investigate if residential agricultural pesticide exposure during gesta

21 whether and how personal exposures relate to residential air pollution estimates, which are normally

22 ationship between long-term (annual average) residential air pollution exposure and BP in the Nationa

23 Active ingredients in residential and agricultural insecticides have changed o

24 , and it had nearly the same impact (24%) as Residential and Commercial (27%) in Europe.

25 ns targeting Land Transportation (ozone) and Residential and Commercial (PM2.5) sectors would particu

26 n mid-latitudes, surface transportation, and residential and commercial combustion from Central and E

27 Residential and commercial fires generate a complex mixt

28 The Residential and Commercial sector had the greatest impac

29 , Land Transportation, Energy, Industry, and Residential and Commercial).

30 combination of long-term (1980-2010) data on residential and energy development across western Colora

31 ate a demographic response in mule deer with residential and energy development at large spatial exte

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

33 es (tree age 8-92 years) were collected from residential and industrial areas near Sauget, IL to iden

34 ssions associated with fuel switching in the residential and industrial sectors leads to increased or

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

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

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

38 ironmental performance of wooden and massive residential and office buildings.

39 increased after bystander defibrillation in residential and public locations.

40 The energy consumption of the residential and public sectors decreased drastically, wh

41 act urban form can result in savings in both residential and transport energy use.

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

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

44 mug/m3 PM2.5 exposures in yearly participant residential annual mean, or in metropolitan area-wide me

45 When adjusted for age, marital status, residential area, clinical characteristics, and copaymen

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

47 rate of these rodent species in the field or residential area.

48 samples with 22 PAH compounds obtained from residential areas close to industrial parks in central T

49 l-being, but different individuals may value residential areas differently.

50 te matter (PM) air pollution exposing nearby residential areas forms several European air pollution h

51 rations of ambient fine particles (PM2.5) in residential areas where wood combustion is common for re

52 rations were downwind from the plant site in residential areas, but both were among the farthest away

53 conventional farming, in close proximity to residential areas, may adversely affect children's respi

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

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

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

57 Children's residential black carbon concentrations were estimated b

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

59 ct fluorescent lights (CFL) commonly used in residential buildings; fluorescent tubes common in indus

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

61 clusters of 3-4 households, within the wider residential camps, which vary in size.

62 lower for those in floating outreach than in residential care (-0.424, -0.734 to -0.114, p=0.007).

63 those in supported housing than for those in residential care (0.145, 0.010 to 0.279, p=0.035).

64 The mean annual budget was pound466 687 for residential care (range pound276 000-777 920), compared

65 ity of life was similar for service users in residential care and supported housing (mean difference

66 Those in residential care and supported housing had more severe m

67 checkups of 126 inhabitants of five Austrian residential care facilities were analyzed.

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

69 Residential care was most expensive but provided for peo

70 619 service users were recruited from 22 residential care, 35 supported housing, and 30 floating

71 es from 14 nationally representative regions-residential care, supported housing, and floating outrea

72 ded but experienced more crime than those in residential care.

73 ervals using an autosampler installed at the residential catchment outlet pipe that drained 31 low-de

74 transport in the stormwater runoff from the residential catchment was driven by mixing of multiple s

75 resolution data elucidating N sources in the residential catchments are not available.

76 the first such analysis of bone from a full residential-ceremonial complex and evaluates multiple hy

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

78 re the importance of past as well as current residential circumstances for cardiometabolic health.

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

80 Residential combustion (RC) and electricity generating u

81 to PM2.5- and O3-related health burden from residential combustion and electricity generating unit e

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

83 remature deaths in China are attributable to residential combustion emissions, approximately a third

84 large portion of air pollutants result from residential combustion of solid biomass and coal fuel fo

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

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

87 us is associated with characteristics of the residential community where he or she resides.

88 laza and consisting of both governmental and residential components.

89 e investigated the associations of long-term residential concentrations of ambient particulate matter

90 ic Study of Atherosclerosis and assigned 5-y residential concentrations of PM10-2.5 mass, copper, zin

91 that central monitoring sites can represent residential conditions when locations are well chosen wi

92 vironmental health messaging strategies with residential consumers.

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

94 aerodynamic diameter of <10 mum [PM10]) for residential, daycare, and school addresses during the li

95 activity in the single variable models: net residential density (exp[b] 1.006 [95% CI 1.003-1.009];

96 esity (WHO criteria of BMI >/=30 kg/m(2)) on residential density (units per km(2)), adjusting for act

97 tified more pronounced protective effects of residential density among individuals who were younger,

98 The fitted restricted cubic spline adiposity-residential density dose-response curve identified a tur

99 Beyond 1800 units per km(2), residential density had a protective effect on adiposity

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

101 er, the evidence for identifying the optimum residential density in relation to obesity has been far

102 sponse curve identified a turning point at a residential density of 1800 residential units per km(2).

103 Below a residential density of 1800 units per km(2), an incremen

104 were significantly associated with perceived residential density, land use mix-access, street connect

105 vement networks, achieving optimum levels of residential density, reducing distance to public transpo

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

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

108 One of these hot-spot is the residential district of Ostrava Radvanice-Bartovice with

109 were recorded on the ground downwind in the residential district when wind speeds >1 ms(-1).

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

111 We assess residential electricity and natural gas demand in Los An

112 s, we find that without policy intervention, residential electricity demand could increase by as much

113 nsitivity analysis to estimate the impact of residential emissions from cooking and heating activitie

114 fe years attributable to PM2.5 exposure from residential emissions.

115 ipheral leukocyte count may be influenced by residential endotoxin exposure in diverse settings.

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

117 We calibrate residential energy use against metered data, accounting

118 We find that emissions from residential energy use such as heating and cooking, prev

119 bout their transport modes during each trip (Residential Environment and Coronary Heart Disease (RECO

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

121 aim was to evaluate the association between residential exposure to vehicular traffic and breast can

122 active wells, the risk estimated for maximum residential exposure was 0.04 in a million, which is bel

123 od, representing cumulative occupational and residential exposure, showed increased odds of ALS for 2

124 Occupational and residential exposures to environmental toxins, and blood

125 ompleted a survey assessing occupational and residential exposures.

126 mphetamine dependence and were enrolled in a residential facility, where they maintained abstinence f

127 n models to explore associations between the residential food environment and fruit and vegetable int

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

129 In addition, California's residential furniture flammability standard (TB-117) has

130 , utility vehicles, urban buses, semitrucks, residential gas furnaces, and natural-gas-fired power pl

131 ards models to estimate associations between residential greenness (as a continuous variable) and mor

132 and to characterize the potential impact of residential greenness and air pollution on asthma trajec

133 examine the prospective association between residential greenness and mortality.

134 Although residential greenness appears to be associated with chil

135 Residential greenness was defined as the mean Normalized

136 INTERPRETATION: Increased amounts of residential greenness were associated with reduced risks

137 cohort-specific and combined associations of residential greenness with allergic rhinitis and aeroall

138 living HGs, with limited relatedness within residential groups embedded in a larger mating network.

139 air pollution due to biomass combustion for residential heating adversely affects vulnerable populat

140 ize the need to mitigate emissions from both residential heating and cooking sources to reduce the he

141 Scenarios run without residential sector and residential heating emissions are used in conjunction wi

142 sources such as industrial stacks, vehicles, residential heating, and forest fires, whereas the PAH c

143 ood burning organic aerosols (OA) from local residential heating.

144 lable credit reporting company, to construct residential histories for participants in the California

145 Residential histories of 1,508 participants with breast

146 approach, however, is limited by the lack of residential histories typically available for study part

147 al fate and transport models and participant residential histories, was analyzed in relation to liver

148 nd sulfur dioxide), derived from participant residential history and ambient air monitoring data, and

149 eled independently of measured PFOA based on residential history and plant emissions.

150 008-2011 reporting demographic, medical, and residential history information.

151 hold coal for cooking was assessed through a residential history questionnaire.

152 l data sources on mortality, school records, residential history, socioeconomic status, and chronic d

153 Indeed, residential homophily in seed exchanges results from loc

154 Residential housing had two times the magnitude of effec

155 expressed by both neurons and microglia, the residential immune cells in the brain.

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

157 tcomes in 8 domains: educational attainment, residential independence, gainful activity, desistance f

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

159 yl sulfonamides (FOSAs), were assessed in 61 residential indoor air and 15 personal air samples colle

160 SAs were detected in 49-70% and 7-13% of the residential indoor air samples, respectively.

161 ll samples, and the median concentrations in residential indoor air were 2970, 10400, and 3120 pg m(-

162 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

163 50% lower than the median concentrations in residential indoor air.

164 BzP) and di-2-ethylhexyl phthalate (DEHP) in residential indoor environments and the influence of tem

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

166 s (>32%), dropping out of school (>57%), and residential instability (51%).

167 results, we used the pooled GMs to calculate residential intake from dust ingestion, inhalation, and

168 Several phthalates and RFRs had the highest residential intakes.

169 Exposure data at the residential level were provided by a chemical transport

170 gy and water efficiency opportunities at the residential level, including both direct and indirect co

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

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

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

174 e also exhibit high similarity regardless of residential location in urban or rural counties.

175 Both indigenous race and residential location influenced patient survival, with a

176 with nonindigenous recipients, whereas rural residential location is associated with patient but not

177 Residential location is thought to influence people's we

178 It is unclear whether rural versus urban residential location might contribute to this.

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

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

181 Patients' residential location was classified as urban (major city

182 Residential location was determined by the last known 5-

183 Residential location was not associated with graft survi

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

185 in a public location and 13905 (74.4%) in a residential location.

186 chemical eye injuries most commonly occur in residential locations (10.3% [n = 14772]; 95% CI, 9.6%-1

187 bystander defibrillation remained limited in residential locations.

188 PM2.5 concentration, than in the low-density residential LULC.

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

190 onnaire data on demographics, behaviour, and residential malaria risk factors, and we also assessed g

191 were randomized to either a 3-day intensive residential mindfulness meditation or relaxation trainin

192 chival data verifies that contexts with high residential mobility indeed have less out-group hostilit

193 The residential mobility patterns of modern hunter-gatherers

194 d argument about when to depart camps, Batek residential mobility seems to maximize group-level forag

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

196 foraging related to the emergent property of residential movements.

197 C) and regression models to predict PNC in a residential neighborhood (Somerville) and an urban cente

198 ungunya transmission dynamics within a large residential neighborhood, explicitly accounting for huma

199 Mean annual residential nitrogen dioxide (NO2) exposure was estimate

200 ining sites influenced model performance and residential NO2 exposure estimates for a cohort of 13679

201 This research explored the trade-off between residential NPR systems using a life-cycle approach to a

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

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

204 the type, location, timing, and frequency of residential pesticide use.

205 Maternal residential PM2.5 (particles with an aerodynamic diamete

206 Maternal residential PM2.5 exposure during pregnancy was estimate

207 highly exposed to ticks in comparison with a residential population and a historic sample.

208 compared with a matched cohort composed of a residential population and blood samples from forest ser

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

210 n applicators and animals, but the effect on residential populations, and especially on children livi

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

212 We mapped nearest O&G well to residential properties to evaluate population size, temp

213 ble to traffic density, 430 deaths (2.4%) to residential proximity to a major road, and 690 (3.7%) to

214 We tested associations between residential proximity to a major roadway and PM2.5 expos

215 Residential proximity to agricultural pesticide use has

216 used regression models to evaluate prenatal residential proximity to agricultural use of five potent

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

218 evaluated the relationship between prenatal residential proximity to agricultural use of potentially

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

220 associations of childhood leukemia with both residential proximity to gasoline stations and exposure

221 Residential proximity to gasoline stations or automobile

222 nts' exposures to TRAP using two surrogates: residential proximity to major roads (1993 onwards) and

223 aimed to investigate the association between residential proximity to major roadways and the incidenc

224 Residential proximity to major roadways during gestation

225 udies have assessed the associations between residential proximity to power plants and adverse birth

226 Residential proximity to road traffic volumes and traffi

227 Residential proximity to roadway and prior-year and life

228 Studies of lung cancer related to residential proximity to roadways and NOx also suggest i

229 Our results highlight the need to consider residential proximity to roadways as a potential cardiov

230 amined the association between participants' residential proximity to solid-waste facilities with pot

231 5 and all active power plants and determined residential proximity to the nearest power plant for eac

232 ns, the best-fit models included kinship and residential proximity, exchanges in kind and across doma

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

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

235 randomized clinical trial was conducted in a residential research setting with 103 participants with

236 patients' information and captured field and residential rodents in Qingdao City, China from 2010 to

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

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

239 for 0.5-6 years (2.2 +/- 1.5 years) from two residential schools.

240 Scenarios run without residential sector and residential heating emissions are

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

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

243 on activities in winter, especially from the residential sector.

244 Black residential segregation has been declining in the United

245 Ethnoracial residential segregation is a complex, multiscalar phenom

246 ggests that neighborhood-level racial/ethnic residential segregation is linked to health, but it has

247 acks and other Americans with decline in the residential segregation of blacks.

248 tified by levels of metropolitan area racial residential segregation, classified using a multigroup d

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

250 modifying role of metropolitan level racial residential segregation.

251 9,727), results adjusted for confounders and residential self-selection revealed fewer significant co

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

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

254 eness of routine air monitoring stations for residential sites in these areas.

255 Pleistocene residential sites with multiple contemporaneous human bu

256 ve PCB distribution and apparent movement to residential sites, where 24 of 27 samples were collected

257 Residential solid fuel use contributes to degraded indoo

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

259 institution, returned to their preadmission residential status 6 months after nonelective abdominal

260 % of patients returned to their preadmission residential status and 22% were institutionalized.

261 Understanding the impact of surgery on residential status and risk factors for institutionaliza

262 Residential status before admission, at discharge, and 6

263 Change in residential status was associated with decreased quality

264 luding age, sex, race, Medicaid eligibility, residential status, hospital volume, ruptured abdominal

265 patients had returned to their preadmission residential status.

266 ts them from returning to their preadmission residential status.

267 ople with the disorder, life expectancy, and residential status.

268 tand the sources and transformations of N in residential stormwater runoff.

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

270 ct, limiting the elevation of commercial and residential structures in D.C. to 130 feet.

271 reducing opioid withdrawal symptoms during a residential tapering program.

272 ion and number of CHD events attributable to residential traffic density, proximity to a major road,

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

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

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

276 on in abstinent participants with CUD before residential treatment discharge and in 20 healthy matche

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

278 important gap of the energy-water nexus in a residential unit and provides a decision making tool for

279 Residential unit density was objectively assessed within

280 rning point at a residential density of 1800 residential units per km(2).

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

282 propoxur (-34%), which is currently sold for residential use but with increased restrictions since 19

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

284 bility, and changes in regulations governing residential use of OPs during the study periods.

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

286 e importance of paraoccupational, drift, and residential use pathways.

287 Residential use was common in the United States before 2

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

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

290 hree of four insecticides no longer sold for residential use: chlordane (-15% per year), chlorpyrifos

291 -transfer model is coupled with a stochastic residential water demand generator to investigate the ef

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

293 t the scale of individual streets within one residential watershed.

294 We estimate that the aqSOA from residential wood combustion can account for up to 0.1-0.

295 tates with large populations and significant residential wood combustion dominate RC health impacts.

296 Residential wood combustion emissions are one of the maj

297 cancer compared with matched (age, sex, and residential ZIP code) noncancer controls (n = 73,545) wi

298 We obtained pediatric ED visits geocoded to residential ZIP codes for visits with nonmissing PM2.5 e

299 Mothers whose residential zip codes were within 10 km of a meteorologi

300 age, or 0.38 when adjusted for sex, age, and residential zone.