ライフサイエンスコーパス: indoor

1 00-1.45) compared with those who did not tan indoors.

2 skin cancer screening in individuals who tan indoors.

3 and polypropylene deposition plates deployed indoors.

4 oxyl and peroxy radicals (OH and HO2, "HOx") indoors.

5 ), compared with individuals who did not tan indoors.

6 of respondents were women who usually worked indoors.

7 and organic (57.2+/-3.2mug/kg) compared with indoor (40.2+/-3.1mug/kg) (P<0.001), which was perhaps r

8 because of both the amount of time we spend indoors (~90%) and the ability of buildings to positivel

9 f hyperglycemia based on different levels of indoor activity (<5.0, 5.0-6.9, and >/=7.0 hours/day) we

10 besity, and an inverse association of either indoor activity or sleeping time with the risk of hyperg

11 glycemia associated with different levels of indoor activity, outdoor activity, TV watching, and slee

12 Perinatal indoor aeroallergen exposure does not seem to affect dev

13 None of the other indoor aeroallergens were associated with worsening asth

14 Indoor aeroallergens, including rat, mouse, cockroach, c

15 dents were collected and analyzed for common indoor aeroallergens.

16 st observation of multiday persistence of an indoor aerosol transformation linked to a kitchen degrea

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

18 e-DBE-DBCH) were more frequently detected in indoor air (detection frequencies >60%), while less vola

19 etardants (LFRs) were measured in samples of indoor air (n = 35) and indoor dust (n = 77) from UK hom

20 des (FOSAs), were assessed in 61 residential indoor air and 15 personal air samples collected in Oslo

21 All target compounds were detected in indoor air and dust samples.

22 ganophosphate esters (OPEs) by clothing from indoor air and transfer via laundering to outdoors were

23 try of squalene contained within skin oil to indoor air chemistry, the surface reaction of squalene w

24 ous ozonolysis of squalene, a key species in indoor air chemistry.

25 owed a significant concentration increase in indoor air concentrations during computer installation a

26 amples from farmworker households had higher indoor air concentrations of both pesticides than did sa

27 Overall, indoor air concentrations were lower than outdoors.

28 hat source introduction was not reflected in indoor air concentrations.

29 port rates are higher and can lead to higher indoor air concentrations.

30 The linking of indoor air exposures with health outcomes provides a dat

31 Indoor air in contaminated buildings may confer airborne

32 ese "clean" Petri dishes and foil squares to indoor air in two different residences for successively

33 Predicted contributions to indoor air levels were higher than those in the resident

34 t buildings (n = 37,185; 19% exposed), where indoor air PCB concentrations have been measured were cr

35 Indoor air PCBs are generally less chlorinated than PCBs

36 with skin aging, but no direct link between indoor air pollutants and skin aging manifestations has

37 Little is known about the impact of indoor air pollution from wood-burning stoves or firepla

38 community household socioeconomic position, indoor air pollution, previous tuberculosis among househ

39 ry fine particles and their contributions to indoor air quality deterioration were examined by collec

40 ke, an air-filter intervention that improved indoor air quality did not affect quality-of-life measur

41 Randomized controlled trials to improve indoor air quality in homes of children with asthma are

42 elds, such as automobile, aerospace, safety, indoor air quality, environmental control, food, industr

43 one of the important factors that affect the indoor air quality.

44 te ventilation, it will still result in poor indoor air quality.

45 Indoor air samples were collected during several periods

46 ected in 49-70% and 7-13% of the residential indoor air samples, respectively.

47 and the median concentrations in residential indoor air were 2970, 10400, and 3120 pg m(-3) for 6:2,

48 Indoor air where people spend 65-90% of their time is al

49 bw(-1) day(-1) were obtained in residential indoor air, while 1.0, 0.10, 3.3, 0.33, 0.88, and 0.09 p

50 ncentrations and profiles of contaminants in indoor air.

51 portant yet overlooked source of terpenes in indoor air.

52 han the median concentrations in residential indoor air.

53 with that produced by long-term exposure to indoor air.

54 Research on the sources of indoor airborne chemicals has traditionally focused on o

55 ntrol determinants have been associated with indoor allergen sensitization.

56 Concentrations of 8 indoor allergens (Alt a 1, Bla g 1, Can f 1, Fel d 1, De

57 ude chronic asthma and exposure to perennial indoor allergens and asthma related to fungal infection.

58 ate climate zones and an important source of indoor allergens causing allergic asthma and rhinitis in

59 Although sensitization to indoor allergens is strongly associated with asthma, the

60 Early-life sensitization to indoor allergens predicts asthma development.

61 ntial solid fuel use contributes to degraded indoor and ambient air quality and may affect global sur

62 lance approach for quantifying exposure from indoor and ground-level urban and rural outdoor sources

63 Dynamic indoor and human physicologically based pharmacokinetic

64 Mean indoor and outdoor air concentration ratios for chlorpyr

65 Here we report indoor and outdoor air concentrations of PCBs and OH-PCB

66 toms (LC-PCBs) due to their presence in both indoor and outdoor air.

67 ion-to-exposure archetypes range from global indoor and outdoor averages, via archetypal urban and in

68 were surveyed at random locations within 25 indoor and outdoor categories.

69 phase chemistry of organic molecules in both indoor and outdoor environments.

70 Passive sampling for indoor and outdoor exposures to chlorpyrifos, azinphos-m

71 widely recognized as an important source of indoor and outdoor particle and volatile organic compoun

72 ofile of human subjects engaged in prolonged indoor and outdoor physical activities, and to make a re

73 enriched relative to the local soil both in indoor and outdoor PM2.5 demonstrating their noncrustal

74 oid concentrations in the majority of paired indoor and outdoor PM2.5.

75 sure to fine particulate matter (PM2.5) from indoor and outdoor sources is a leading environmental co

76 We report comparative indoor and outdoor stability testing of organic solar ce

77 wever they still persist in the environment, indoors and in humans.

78 venting malaria where vectors primarily bite indoors and late at night, but their effectiveness is un

79 h data loggers and mosquitoes were collected indoors and outdoors using Furvela tent traps and were i

80 variety of carboxylic acids were identified indoors and outdoors, including monoacids, diacids, hydr

81 m passive air samplers deployed outdoors and indoors and polypropylene deposition plates deployed ind

82 hours of the evening, before individuals are indoors and protected by bednets, followed by a return t

83 cream made from milk obtained from cows fed indoors, and by early or late grazing, in alpine rangela

84 d exposure indoors, the amount of time spent indoors ( approximately 95%), and the mode and duration

85 We found that indoor arthropod diversity is strongly influenced by acc

86 These findings suggest that indoor arthropods serve as a connection to the outdoors,

87 The indoor biome is a novel habitat which recent studies hav

88 The indoor built environment plays a critical role in our ov

89 Indoor burning of fuel for heating or cooking releases c

90 ysis is not likely an important fate for NO3 indoors, but NO2 photolysis could be an important source

91 nments (humidity, O3, and NOx) using both an indoor chamber and an outdoor chamber.

92 materials, evidence for acid production from indoor chemical reactions with ozone was found.

93 tile organic compounds (VOCs) and influences indoor chemistry.

94 In children with asthma, indoor classroom NO2 levels can be associated with incre

95 We aimed to determine the effect of indoor classroom NO2 on lung function and symptoms in in

96 scale smart membranes needed for sustainable indoor climate control.

97 ty and temperature, are important to achieve indoor climate regulation.

98 e and two-storey buildings provided a cooler indoor climate than did traditional housing, two-story b

99 a, to decrease mosquito density and regulate indoor climate.

100 Bla g 2 is a major indoor cockroach allergen associated with the developmen

101 To discover potential biomarkers of indoor combustion products, we profiled adducts at the C

102 amma-GluCys in nonsmoking females exposed to indoor-combustion products in Xuanwei and Fuyuan, China.

103 istribute from its original sources to other indoor compartments, including clothing.

104 The average indoor concentration of carboxylic acids was 6.8 ppb, of

105 AER (Tier 1), infiltration factors (Tier 2), indoor concentrations (Tier 3), personal exposure factor

106 In addition, some carboxylic acids measured indoors correlated to CO2 in daytime, suggesting that hu

107 e case than the control group if they tanned indoors (crude OR, 6.0; 95% CI, 1.3-28.5).

108 wheezing, including airborne viruses, smoke, indoor dampness, cockroaches, and poor access to health

109 played a single daytime peak, those measured indoors displayed a daytime and a nighttime peak.

110 Whether the child lived with an indoor dog in the first year of life was assessed throug

111 asured in samples of indoor air (n = 35) and indoor dust (n = 77) from UK homes and offices.

112 /electronic equipment that contained RDP and indoor dust collected on and around surfaces of this equ

113 Our results indicate that U.S. indoor dust consistently contains chemicals from multipl

114 To virtually screen indoor dust contaminants and their metabolites for THDCs

115 Indoor dust is a reservoir for commercial consumer produ

116 e to the microbial and allergenic content of indoor dust is associated with adverse and protective he

117 We systematically searched the U.S. indoor dust literature on phthalates, replacement flame

118 3T3-L1 cells were exposed to extracts of indoor dust or individual SVOCs and assessed for triglyc

119 ological matrices of the exposed workers and indoor dust samples.

120 and assessing the microbiome composition of indoor dust samples.

121 products are for the first time reported in indoor dust.

122 indicate that all of these may be sources to indoor dust.

123 current state of science with respect to the indoor environment and its effects on the development an

124 ance for future research in the study of the indoor environment and on environmental interventions as

125 new pathway for MEA exposure of people in an indoor environment.

126 lower-chlorinated, semi-volatile PCBs in the indoor environment.

127 s from exposure to semi-volatile PCBs in the indoor environment.

128 of estrogenic compound contamination in the indoor environment.

129 Indoor environmental allergen exposure during early life

130 tion in national asthma guidelines to target indoor environmental exposures, most insurers generally

131 payment of the goods and services needed for indoor environmental interventions for their patients wi

132 We simulated indoor environmental quality (IEQ) conditions in "Green"

133 fraction of cigarette smoke that persists in indoor environments after smoking.

134 With high detection in indoor environments and increasing toxicological evidenc

135 Exposure to moldy or damp indoor environments is associated with allergic disease

136 ionizing, organic chemical concentrations in indoor environments resulting in delivered tissue doses

137 cts of cooking, heating, and wood burning in indoor environments, and, more recently, products genera

138 and adipates) were installed in residential indoor environments.

139 ions potentially encountered in contaminated indoor environments.

140 t are commonly encountered every day in many indoor environments.

141 iderable negative impacts on human health in indoor environments.

142 rs under real-use conditions in a variety of indoor environments.

143 OCs) that are often ubiquitously detected in indoor environments.

144 the microbial and chemical components of the indoor exposome.

145 the biologic properties of indoor exposures, indoor exposure assessment, and exposure reduction techn

146 Information on human indoor exposure is necessary to assess the potential ris

147 aximize comparability of studies and advance indoor exposure science.

148 ndividually weighted estimates accounted for indoor exposure to ambient PM2.5.

149 effect on indoor nitrate also causes higher indoor exposure to fine nitrates.

150 Indoor exposure typically contributes 80-90% to overall

151 new insights into the biologic properties of indoor exposures, indoor exposure assessment, and exposu

152 d feeding period and not in samples from the indoors feeding period.

153 Increasing evidence implicates high indoor fungal exposures as a precipitant of asthma in ch

154 h yet to be discovered about their impact on indoor health and the unique ecological dynamics within

155 Participants completed questionnaires on indoor heating and cooking practices for both their enro

156 ted the risk of breast cancer in relation to indoor heating and cooking practices.

157 ervals (95% CIs) for the association between indoor heating/cooking and breast cancer.

158 Analytes included four insecticides sold for indoor home use during our study period (carbaryl, cyper

159 Indoor horticulture offers a sensible solution for susta

160 of high-powered single-wavelength lasers for indoor horticulture.

161 ought to evaluate the adipogenic activity of indoor house dust extracts and a suite of semivolatile o

162 ent tubes will be important to room-averaged indoor HOx levels due to the strong distance dependence

163 We use these measurements to predict indoor HOx production rates from the photolysis of nitro

164 o charge the battery under both full sun and indoor illumination conditions, and the addition of the

165 Individuals who tanned indoors in the past year were not significantly more lik

166 ge, 39 y), 787 (7.0%) reported having tanned indoors in the past year.

167 ge, 39 y), 787 (7.0%) reported having tanned indoors in the past year.

168 ur results indicated that the level of Cr in indoor industrial dust was more than twice, compared to

169 particle production from exposure to common indoor levels of ozone (23 +/- 2 ppb).

170 Among high-risk inner-city children, higher indoor levels of pet or pest allergens in infancy were a

171 Indoor lifetime testing was performed on solar cells usi

172 ed photon fluxes and distance dependences of indoor light sources including halogen, incandescent, an

173 ighlight their potential for infiltration of indoor living environments.

174 accumulation and release of the chemical in indoor media and tissues of the exposed subject.

175 al/annual) in the laboratory, in tanks in an indoor mesocosm facility, and in coastal mesocosms under

176 were close to unity providing evidence that indoor metal-bearing PM2.5 had predominantly outdoor ori

177 to characterize the microbial communities of indoor microcosms that were either exposed to each pesti

178 hat would not be properly accounted for with indoor microenvironmental measurements.

179 The Indoor model predictions were also comparable to those f

180 The Indoor model successfully reproduced independently measu

181 The stabilizing effect on indoor nitrate also causes higher indoor exposure to fin

182 ply air the second most important (35%), and indoor nonoccupant emissions the least (8%).

183 2 photolysis could be an important source of indoor O3.

184 ids are ubiquitous in ambient air, yet their indoor occurrence and abundance are poorly characterized

185 ime for oxidation was the same as that in an indoor office with an MRO3 between 22 and 32 ppb, sugges

186 Individuals who tan indoors often exhibited a concurrent tendency to sunburn

187 nclusions and Relevance: Individuals who tan indoors often exhibited a concurrent tendency to sunburn

188 Indoors, only 78% of air samples for chlorpyrifos and 35

189 as realized contact between a person and an indoor or outdoor environment that poses a risk of incre

190 t female malaria mosquitoes, irrespective of indoor or outdoor feeding and resting patterns.

191 e UNEP/SETAC Life Cycle Initiative a coupled indoor-outdoor emission-to-exposure framework to provide

192 pants ages 13 to 20 years matched on sex and indoor-outdoor location at the time of each index case p

193 and rural outdoor sources using an effective indoor-outdoor population intake fraction and a system o

194 an indicator of airway hyperreactivity) and indoor particulate matter (PM) PM2.5.

195 eased in association with <800mug FA and any indoor pesticide exposure {adjusted odds ratio [OR]=2.5

196 d with low FA [OR=1.2 (95% CI: 0.7, 2.2)] or indoor pesticides [OR=1.7 (95% CI: 1.1, 2.8)] alone.

197 exposure to environmental tobacco smoke, and indoor pets.

198 Here we directly measured the indoor PM2.5 exposure in 30 households in Taizhou, China

199 Our study provided evidence that the indoor PM2.5 exposure is associated with skin aging mani

200 nitial examination group, we showed that the indoor PM2.5 exposure levels were positively associated

201 owed a 67% (95% CI: 50% to 77%) reduction in indoor PM2.5, but no change was observed with the improv

202 HONO is also a major indoor pollutant that threatens human health.

203 clododecane (HBCD) has been recognized as an indoor pollutant.

204 nic compounds (SVOCs), an important class of indoor pollutants that may have significant adverse effe

205 red PM2.5 exposure and questionnaire data of indoor pollution sources, we built a regression model to

206 natural gas development were associated with indoor radon concentrations.

207 Indoor residual spraying (IRS) and long-lasting insectic

208 Long-lasting insecticidal nets (LLINs) and indoor residual spraying (IRS) have contributed substant

209 Although indoor residual spraying (IRS) is an effective tool for

210 s (LLINs) alone or LLINs in combination with indoor residual spraying (IRS) with a pyrethroid (deltam

211 ng-lasting insecticide treated nets (LLINs), indoor residual spraying (IRS), and artemisinin combinat

212 al, with seasonal malaria chemoprevention or indoor residual spraying added second depending on seaso

213 Indoor residual spraying coverage per cluster was more t

214 e points (95% CI 0.86-15.83) and coverage of indoor residual spraying increased by 6.63 percentage po

215 to its detrimental impact on the ecosystem, indoor residual spraying of DDT is still recommended for

216 Long-lasting insecticidal nets (LLINs) and indoor residual spraying of insecticide (IRS) are the pr

217 (HIV)-uninfected pregnant women protected by indoor residual spraying of insecticide (IRS).

218 ed pregnant women in an area of Uganda where indoor residual spraying of insecticide had recently bee

219 IV-infected pregnant women in the setting of indoor residual spraying of insecticide, adding monthly

220 ster was more than 80% for both years in the indoor residual spraying plus LLIN group.

221 on of long-lasting insecticide-treated nets, indoor residual spraying, and focal mass drug administra

222 , gender, insecticide-treated net (ITN) use, indoor residual spraying, household wealth, and geograph

223 ed vector control tools such as bed nets and indoor residual spraying.

224 ol tools such as insecticide treated nets or indoor residual sprays target mosquitoes in human dwelli

225 Vector control tools that target indoor-resting mosquitoes, such as bednets and insectici

226 d physical performance by power output on an indoor rowing ergometer.

227 and exposures were predicted for two typical indoor scenarios: a home and a bar.

228 ing that O3 was the dominant oxidant in this indoor setting.

229 d outdoor averages, via archetypal urban and indoor settings, to 3646 real-world cities in 16 paramet

230 oupled plasma-mass spectrometry, we captured indoor signatures of outdoor episodic emissions arising

231 a dynamic process that can serve as a major indoor source of biological particulate matter (bioPM).

232 nly Co had an I/O abundance ratio >1 but its indoor sources could not be explicitly identified.

233 fractions from residential and occupational indoor sources range from 470 ppm to 62000 ppm, mainly a

234 Besides indoor sources such as off-gassing of building materials

235 " (shared conversation) and "casual" (shared indoor space) social contacts in 16 Zambian communities

236 ich is used to estimate transmission risk in indoor spaces.

237 Air (indoor stationary air and personal ambient air), dust (f

238 Sixty indoor stationary air samples, 13 personal air samples,

239 roduction system (organic vs. free range vs. indoor), supermarket and purchase date on the concentrat

240 ogress in understanding sorption of SVOCs on indoor surfaces.

241 ip between surface roughness and K for clean indoor surfaces.

242 gnificantly affect the fate and transport of indoor SVOCs and the resulting human exposure.

243 ng individuals aged 18 to 34 years, frequent indoor tanners (>/=10 times in the past year) were more

244 justed model: 82.3% (95% CI, 77.9%-86.0%) of indoor tanners had at least 1 sunburn during the precedi

245 Evidence suggests that indoor tanners may be more inclined to adopt poor photop

246 years, P < .001) and reported more frequent indoor tanning (median number of sessions, 100 vs 40, P

247 48.9%-58.4%) of those who did not engage in indoor tanning (P < .001).

248 Sex-specific associations for indoor tanning and melanoma by anatomic site were examin

249 ongitudinal study of the association between indoor tanning and melanoma in a large cohort of Norwegi

250 d age- and sex-specific associations between indoor tanning and melanoma to determine if these trends

251 dence of a dose-response association between indoor tanning and risk of melanoma and supports the hyp

252 f indoor tanning and the association between indoor tanning and sunburn among US high school students

253 e needed to further reduce the prevalence of indoor tanning and sunburn and thus prevent future cases

254 Indoor tanning and sunburns, particularly during adolesc

255 To examine the trends in the prevalence of indoor tanning and the association between indoor tannin

256 years, women younger than 40 years initiated indoor tanning at a younger age (16 vs 25 years, P < .00

257 The strongest OR for indoor tanning by anatomic site was for melanomas arisin

258 ents in the United States, the prevalence of indoor tanning decreased from 15.6% (95% CI, 13.7%-17.6%

259 athing vacations and were more likely to use indoor tanning devices.

260 were calculated for melanoma in relation to indoor tanning exposure for men and women by diagnosis o

261 bjective: To examine the association between indoor tanning frequency and behaviors related to skin c

262 To examine the association between indoor tanning frequency and behaviors related to skin c

263 the literature exist in young adults and by indoor tanning frequency.

264 Despite declines in the prevalence of indoor tanning from 2009 to 2015 among high school stude

265 Three-quarters of those who engaged in indoor tanning had experienced at least 1 sunburn.

266 with melanoma risk and examined the role of indoor tanning in age at melanoma diagnosis.

267 Prevalence of indoor tanning in the past year from 2009 to 2015 and it

268 risk and linear regression to examine age of indoor tanning initiation in relation to age at diagnosi

269 Indoor tanning is a likely factor for the steeper increa

270 Indoor tanning is associated with increased risk of mela

271 that vulnerability to the harmful effects of indoor tanning is greater at a younger age.

272 Indoor tanning is prevalent among young adults and women

273 Importance: Indoor tanning is prevalent among young adults and women

274 epidemic can be expected to continue unless indoor tanning is restricted and reduced.

275 Moreover, women who started indoor tanning prior to 30 years of age were 2.2 years (

276 en, given the timing of when women initiated indoor tanning relative to diagnosis.

277 2015 among high school students nationwide, indoor tanning remains commonplace among certain subgrou

278 confidence intervals for the relationship of indoor tanning to melanoma risk and linear regression to

279 mine if these trends could be due to greater indoor tanning use among younger women.

280 In 2015, indoor tanning was associated with sunburn in the adjust

281 Decreases in indoor tanning were found among male (from 6.7% in 2009

282 Indoor tanning, defined as any use, first age of use, an

283 ted the associations of age at initiation of indoor tanning, duration of tanning-device use, and dose

284 Hourly measurements of indoor temperature and humidity were recorded in all stu

285 The indoor temperature in the new design houses was 2.3 degr

286 and cooling is a strategy by which to expand indoor temperature setpoint range for large energy savin

287 ates reflect the effects of reduced exposure indoors, the amount of time spent indoors ( approximatel

288 humans spend approximately 90% of their time indoors, the built environment exposome merits particula

289 semivolatile organic compounds (SVOCs) from indoors to outdoors through accumulation from air and th

290 Average indoor-to-outdoor (I/O) abundance ratios for the majorit

291 oncentrations of other insecticides sold for indoor use (carbaryl, cypermethrin, and permethrin) and

292 opoxur) and four that are no longer sold for indoor use including dichlorodiphenyltrichloroethylene (

293 mixed with new scenes and classified them as indoor versus outdoor (encoding task) or old versus new

294 Exposure to indoor VOCs is associated with a range of adverse effect

295 en though this source clearly contributes to indoor volatile organic compounds (VOCs) and influences

296 nt concentrations in bars were modeled using indoor volumes, air exchange rates and the number of hou

297 18 to 60 years, those who frequently tanned indoors were more likely to rarely/never use sunscreen (

298 those in studies of organic film buildup on indoor windows.

299 In this prospective study, using an indoor wood-burning stove/fireplace in the longest adult

300 Having an indoor wood-burning stove/fireplace in the longest adult