ライフサイエンスコーパス: air

1 Concentrations of 17 air pollutants including nitrogen oxides (NOX), particul

2 rful pulsed lasers with peak-intensity above air photoionization and photo-dissociation have demonstr

3 Policies to address air pollution have reduced criteria pollutant emissions,

4 batteries, zinc-air batteries, and aluminum-air batteries.

5 served septal thickening, decreased alveolar air space total volume and, septa surface density.

6 lyses of humid gaseous media such as ambient air and exhaled breath.

7 s that examined associations between ambient air quality and risk of hospitalization for pneumonia in

8 laminar sheath flow of particle-free ambient air and a tunable electric field based on the respective

9 ated with maternal exposure to PM in ambient air during pregnancy.

10 eratures as high as 300 degrees C in ambient air without any encapsulation, is demonstrated.

11 evaluate the reactivity of KO(2) in ambient air.

12 ns of the IHN isomer distribution in ambient air.

13 sters and data reported from a local ambient air monitoring station.

14 ty from exposure to higher levels of ambient air pollution.

15 Inhalation of the ambient air pollutant ozone causes lung inflammation and can sup

16 ation between short-term exposure to ambient air pollution and daily hospital admissions for depressi

17 suggest that short-term exposure to ambient air pollution is associated with an increased risk of da

18 it was not required for growth under ambient air controlled conditions.

19 azoles at room temperature and under ambient air.

20 ims to quantify changes in outdoor (ambient) air pollution exposure from different migration patterns

21 emerging epidemiological associations among air pollution, diabetes, and lung disease.

22 ltralight carbon container floating above an air-dispensing base.

23 pecimens were then individually placed at an air/liquid interface on a stainless-steel grid in cell c

24 ining a digital micromirror device (DMD), an air-free reaction chamber, and microfluidics to independ

25 dance mismatch can be readily realized in an air environment, acoustic waveguiding in an underwater e

26 al polyps (CRSwNP) when differentiated in an air-liquid interface (ALI) usually provide a pseudostrat

27 (pHAE) cultures, which are maintained in an air-liquid interface.

28 Here we report an air- and moisture-stable, visible light-absorbing Zr(IV)

29 Although using an air cathode is the goal for superoxide-based potassium-o

30 n opportunities for reducing the climate and air quality impacts of the AD-composting process.

31 eactive compounds can affect net climate and air quality impacts.

32 aerosol lifetime and thus impact climate and air quality.

33 h correlated with less tracheal collapse and air trapping at end-expiration chest CT.

34 of virus is driven by observed commuting and air travel flows, and use this model to generate influen

35 Conclusion CT measures of emphysema and air trapping increased over 5 years in smokers.

36 fold in the presence of catalytic iodine and air at 40 degrees C in the 1,1,1,3,3,3-hexafluoroisoprop

37 Evaluation of SARS-CoV-2 surface and air contamination during the COVID-19 pandemic in London

38 sive viral RNA contamination of surfaces and air across a range of acute healthcare settings in the a

39 n of premisting (mixing of coolant water and air prior to burr contact) resulted in a significant red

40 No periods of "clean" (nonpolluted) Arctic air were observed.

41 S-Nitrosothiols (RSNOs) serve as air-stable reservoirs for nitric oxide in biology.

42 rofluorocarbon (CFC) banks from uses such as air conditioners or foams can be emitted after global pr

43 When cultured at air-liquid interface, it was possible to follow the migr

44 and alveolar lung mucosa models cultured at air-liquid interface.

45 Lipids in complex, protein-enriched films at air/liquid interfaces reduce surface tension.

46 A well-defined and readily available air-stable dimeric iridium(III) complex catalyzed alpha-

47 ly, alcids varied stroke-plane angle between air and water and chord angle during aquatic flight, exp

48 t all studies suggest an association between air pollution exposure and infant mortality.

49 d turbulence data in the laboratory, in both air and water.

50 The lowest releases to both air and water were recorded for a garment with a very co

51 bility) and packing conditions (cover brine, air or N(2) atmosphere) has been studied to preserve bla

52 ed environmental impact of CO(2) emission by air traffic, aviation particulate emission also deserves

53 o investigated potential causal mediation by air pollution.

54 Emissions of aromatic compounds cause air pollution and detrimental health effects.

55 rge areas of the globe, influencing climate, air quality, and human health in open seas and coast lin

56 (e.g. topography, radiative forcing or cold-air pooling).

57 tu activation of electrode surfaces via cold-air plasma, we show that soft biocompatible materials ca

58 Consolidation, air bronchograms, central lung involvement, crazy paving

59 Low-cost air quality sensors are promising supplements to regulat

60 factors (pollen/flowers [P = .005] and damp air [P = .012]) were more common in asthma.

61 extends reactivity from previously described air-sensitive diorganozinc reagents of limited availabil

62 identified particulate and nitrogen dioxide air pollution inside the home, urine cotinine levels ind

63 Direct air capture (DAC) is positioned to play a critical role

64 tion is directly absorbed by the air (direct air capture) to renew and sustain the carbonate electrol

65 hnologies: postcombustion capture and direct air capture (DAC).

66 dishes with solid media, filter paper discs, air harvesters, and liquid transport media) and assessme

67 ustfonna had the most frequent long-distance air flow, but showed lower amounts of chlorpyrifos and P

68 nitrogen(7-10), in fact represent dominantly air-derived N(2) that experienced (15)N/(14)N fractionat

69 stic times for equilibration exceed the dust-air contact time, and equilibrium is not achieved.

70 Rationale: Although elevated air pollution exposure impairs lung-function development

71 We elucidate the evolution of the entrained air in drop impact on a wide range of liquids, using ult

72 cies to contribute to improved environmental air quality as well.

73 < 0.05) abrupt change in the autumn Eurasian air temperature trend occurred in 2003.

74 Both RMOFs exhibit excellent air and water stability as a result of favorable radical

75 .12-L decrease in the lung volume of exhaled air (95% confidence interval, -0.17 to -0.07; P = 6.62 x

76 g status was biochemically verified (exhaled air CO and serum cotinine).

77 Expanded air transport quality assurance protocols, including a r

78 s ambient levels/~60-120 mug/m3) or filtered air over a 14-week period.

79 Compared to the filtered air group (FA), one-day-exposure-PM(2.5) did not affect

80 particle metrics and MI cases, adjusted for air temperature and relative humidity.

81 n in South Asia has serious consequences for air quality and human/ecosystem health within the region

82 We demonstrate a phase diagram for air evolution regarding hydrodynamics.

83 ted HU were -77 HU for water and -990 HU for air; TEM precision improved with a reduction in variabil

84 urces with population estimates derived from air travel records and census data.

85 quirements desired for water harvesting from air in that it exhibits an S-shaped water sorption isoth

86 ntal niche across the planet, including from air, soil, fresh water, and the oceans.

87 g free convection when calculating t(r) from air temperatures of 2 K above t(r) could introduce a mec

88 ts of several realistic scenarios for future air pollution reductions on lung growth.Methods: Mixed-e

89 ay imaging with sensitivity up to 173 muC Gy(air) (-1) cm(-2) .

90 Cs exhibit high sensitivity of 1652.3 muC Gy(air)(-1) cm(-2) and very low detectable dose rate of 130

91 cted (spatter, settled aerosol, or harvested air), the presence and type of at-source aerosol reducti

92 Guiding light in hollow (air) core fibres offers a potential way to overcome this

93 Far infrared radiation (FIR) and hot air drying (HA) were applied to unpolished and polished

94 We used freeze drying (FD), hot-air drying (HD) at 50 degrees C and sun drying (SD).

95 We collected hourly air pollution and meteorological data from fixed urban b

96 ension and education), others (eg, household air pollution and poor diet) vary by a country's economi

97 xposure-response relationships for household air pollution.

98 In MICs and LICs, household air pollution, poor diet, low education, and low grip st

99 fforts to characterize exposure to household air pollution and for other contexts.

100 hs occur annually from exposure to household air pollution from the use of biomass cooking fuels.

101 e interfaces is recognized in this study: i) air/solution phase acceleration, as is well known in mic

102 ment (UNGD) to adverse health has implicated air pollution and stress pathways.

103 (BC) aerosols perturb climate and impoverish air quality/human health-affecting ~1.5 billion people i

104 Policy interventions to improve air quality can also be in alignment with policies that

105 Improved air quality and human health are often discussed as "co-

106 tem for the complete treatment of ammonia in air with conversion to nitrogen gas without the supply o

107 tterflies responded to fine-scale changes in air temperature, and whether species-specific responses

108 ce, which could contribute to disparities in air pollution and other nuisance exposures.

109 sical properties: intrinsic blinking even in air, excellent fluorescence recovery, and stability over

110 inact) state is stable for more than 40 h in air, highlighting the remarkable resilience of CbHydA1 t

111 work (RMOF) Gd-IHEP-7, which upon heating in air undergoes a single-crystal-to-single-crystal transfo

112 employed atomic force microscopy imaging in air and liquids to visualize ring assembly, DNA binding,

113 AFM imaging in air with controlled humidity preserves the tissue's wate

114 s contributed to significant improvements in air quality, benefiting hundreds of millions of people.

115 ncreases are not mediated by the increase in air pollution.

116 contraction are large body mass, increase in air temperature, loss of natural land, and high human po

117 table over a period of at least 10 months in air.

118 = 4 +/- 1 mA/W), and stability for months in air.

119 ly stable and resistant to bulk oxidation in air.

120 fuels results in up to 65% net reduction in air pollution as we approach 2050, even after accounting

121 tomic force microscopy at high resolution in air and buffer.

122 f chemosensory signaling molecules including air-borne odorants and pheromones.

123 Increased air velocities and stepwise ageing regime had no effect

124 ublic transport strikes and either increased air pollution or worse population health.

125 Increasing air pollution in South Asia has serious consequences for

126 Settled dust from indoor air and outdoor air and direct samples from building mat

127 ting the PM(2.5) levels in well-mixed indoor air.

128 an influence the biological burden of indoor air.

129 This study examined residential indoor air in homes (n = 99) in southeast Louisiana using passi

130 Further study of residential indoor air in low-income women's homes in this area is needed.

131 The indoor air differences between moldy versus no mold homes were

132 s were observed to be correlated with indoor air temperature.

133 ng the partial pressure of oxygen in inhaled air stepwisely (pO(2); 21.25 kPa (0 k), 16.42 kPa (2 k),

134 at a surface, i.e., a topological insulator-air/vacuum interface, have been studied intensely, topol

135 size, succulence and decreased intercellular air space.

136 is the diffusion of CO(2) from intercellular air spaces (IAS) to the first site of carboxylation in t

137 focused on the evolution of the intervening air layer between droplet and substrate during impact, a

138 this reaction for many decades, however, is air-sensitive, prone to photodecomposition, and poorly r

139 lly, waves reflected northward from the ITCZ air column and/or generated by triggered El Nino events

140 ll daughter droplet encapsulated by a larger air shell bubble, forming an antibubble.

141 battery concepts (e.g., Li-ion, Li-S, and Li-air), and we will show opportunities and perspectives as

142 xcellent energy efficiency in a high rate Li-air battery, and iv) high break-down current density for

143 lication of that statement, evidence linking air pollution exposure to cardiovascular health has cont

144 ria formed a dense outer layer at the liquid-air interface of the liquid droplet, protecting the cell

145 batteries, lithium-sulfur batteries, lithium-air batteries, zinc-air batteries, and aluminum-air batt

146 However, the localized air quality improvement was accompanied by a contemporan

147 he ground truth, and is most accurate at low air speeds, within 0.25 +/- 0.60 degrees C.

148 h efficiency (>99.995% PM(0.3) removal), low air resistance (<0.09% atmosphere pressure), high transp

149 ciations between short-term exposure to main air pollutants (fine particulate matter [PM2.5] and ozon

150 on efficiency of OHDCA was highest in marine air, related to the presence of sulfur dioxide and/or or

151 The marine air and continental-marine mixed air had more abundant h

152 All consecutive MASK-air users in 23 countries from 1 June 2016 to 31 October

153 In MASK-air (Mobile Airways Sentinel Network), a visual analogue

154 f the causal role of fine particulate matter air pollution (PM(2.5), or particulate matter <=2.5 mum

155 Cut-open vessels, uncertainties in maximum air volume estimations, sample-length effects, tissue cr

156 metamaterials such as microfabricated metal-air hybrids.

157 (2) is the most promising rechargeable metal-air battery with the combined advantages of low costs, h

158 ficantly altered by both the culture method [air-liquid interface (ALI) vs submerged] and the presenc

159 GVs) have been promoted in China to mitigate air pollution, yet our measurements and analyses show th

160 action of OA in marine (37 +/- 4%) and mixed air (31 +/- 3%), overriding the contributions from BB.

161 The marine air and continental-marine mixed air had more abundant hydroxyl dicarboxylic acids (OHDCA

162 conducted at a thickness of 3, 5, and 7 mm, air velocity of 0.5, 1.25, and 2 m/s, as well as at infr

163 al transformations when contacted with moist air.

164 Here we show a new, air-stable bimetallic scaffold that acts as a single-chr

165 and very low detectable dose rate of 130 nGy(air) s(-1), both desired in medical diagnostics.

166 s C and 210 degrees C for 6 h with nitrogen, air or oil as heat-conducting media.

167 heric half-lives and relatively high octanol-air partitioning coefficients (K(OA)) are likely to have

168 et and substrate during impact, a balance of air compression and drainage within the surface texture,

169 mate the potential public health benefits of air pollution interventions in exposed populations.Objec

170 antification of potential health benefits of air quality improvement.

171 n average, we find that 41 to 53 per cent of air-quality-related premature mortality resulting from a

172 light from acoustically-induced collapse of air bubbles in water, is an efficient means of generatin

173 leaning can greatly alter the composition of air in indoor environments.

174 the design principles for the development of air-stable solid electrolytes.

175 Analyses of the frequency distribution of air pollution events indicate that Fort McKay is regular

176 even greater importance that the effects of air pollutant exposure on human skin be investigated.

177 current understanding of combined effects of air pollution and meteorological variables on adverse bi

178 Evidence regarding the impact of air pollution on acute respiratory distress syndrome (AR

179 ance of research to understand the impact of air pollution on human health, commenting on a study by

180 y, exposure to the world's highest levels of air pollution, highly prevalent pretransition forms of H

181 ic pollution represents a complex mixture of air chemicals that continually interact and transform, m

182 hweight z-scores and exposure to mixtures of air pollutants, where up to -0.21 or approximately a 96

183 -based approach relying on a small number of air quality standards as the only tool to assess risk.

184 d by four people, the total OH reactivity of air was quantified, together with multiple VOCs measured

185 th India and explored the mediating roles of air pollution, physical activity, and stress in these as

186 alculated the radioactivities at the time of air sampling retrospectively based on a previously estab

187 The notable features such as the use of air that is considered as a benign oxidant and EtOH as a

188 We used data on the volume of air travel departing from airports in the infected provi

189 , we characterize the impacts of COVID-19 on air pollution using NO(2) and Aerosol Optical Depth (AOD

190 idential histories and environmental data on air monitoring and simulated atmospheric chemistry, we u

191 ldfires have a significant adverse impact on air quality in the United States (US).

192 heet, either indirectly, by its influence on air temperatures and winds, or directly, mostly through

193 rrigation cooling effect is also observed on air temperature (-0.38 to -0.53 degrees C) from paired f

194 an Heart Association scientific statement on air pollution and cardiovascular disease in 2010, unequi

195 e these interventions in the face of ongoing air pollution exposure.

196 Research took place in the open-air B4WarmED experiment in Minnesota.

197 ts based on social costs of carbon and other air pollutant emissions highlights the importance of gro

198 Outdoor air pollution is a growing public health concern, partic

199 Settled dust from indoor air and outdoor air and direct samples from building materials with mold

200 s-sectionally), including indoor and outdoor air pollutants, built environment, green spaces, tobacco

201 ntal matrices including indoor dust, outdoor air particulates, sea sediment, and river water.

202 bustion and household ventilation on outdoor air pollution has not been assessed.

203 the effect of a high-efficiency particulate air filter attachment on ABS emissions and particle chem

204 Fine particulate air pollution <2.5 mum in diameter (PM(2.5)) is a major

205 We previously assessed indoor and personal air pollution exposures in this area; however, the influ

206 luded the unavailability of data on personal air pollution exposures.

207 sponses in relation to real-world, gas-phase air mixtures.

208 raws upon source apportionment photochemical air quality modeling to characterize the contribution of

209 Ozone, a major contributor to poor air quality, has an array of adverse effects on human, a

210 ring this 19-year period, CO(2) rose 40 ppm, air temperature increased by 1 degrees C and annual rain

211 go structure acting as a valve that prevents air from spreading between tracheids, although the exten

212 nding potential health impacts, prioritizing air pollution mitigation strategies, and enabling global

213 corporation into HVAC ducts or recirculating air purifiers.

214 teria pollutant emissions, improved regional air quality, and benefited public health.

215 (PS) for drug delivery over the respiratory air-liquid interface: the interfacial delivery.

216 ogy; a decoupling of tree growth from rising air temperatures since the 1970s.

217 PCR-confirmed SARS-CoV-2 infection and room air oxygen saturation <=94% whose clinicians requested r

218 for 72 h and then allowed to recover at room air for two weeks (at PND18), sacrificed, and lung hypoa

219 I, 2-minute resting state at baseline (room air); phase II, 6-minute maternal hyperoxia with 100% ox

220 w dose far-UVC lighting to disinfect in-room air has been proposed.

221 ed two-phase flow, consisting of the sampled air stream and a stream of collection medium, is formed

222 t analyses, higher concentrations of several air pollutants during pregnancy or childhood were associ

223 (2.5) concentrations frequently cause severe air pollution events in Delhi.

224 essing precursors, scaling calculations show air-cleaning prevented ~3.4 mg/h of indoor SOA formation

225 on for accelerated reactions at the solution-air interface.

226 e to tremendous impedance mismatch at stable air/water interfaces, viz., the Cassie-Baxter state is d

227 electrophysiological activity using a still-air olfactometer and electroantennography, respectively.

228 and commercial planar cellulose substrates (air-laid paper, cellulose paper, and cotton fabric) is r

229 dings contribute to literature that suggests air quality rules aimed at SO(2) and NO(x) emissions ind

230 Mean summer air temperature (MSAT) was the principal factor driving

231 hile our model simulations support a surface air temperature response to the eruption of the order of

232 1- degrees C increase in global mean surface air temperature.

233 tor compounds were used to isolate sustained air pollution "events".

234 pider-web-inspired network generator (SWING) air filters.

235 e warming treatment, tracking variation in T(air) .

236 Our results establish that air temperature is a necessary but not sufficient variab

237 We provide large-scale evidence that air pollution, specifically ozone, is associated with de

238 The findings suggested that air pollution was causally associated with mortality, ev

239 The air volume fraction (AVF) was estimated from relative si

240 As the air electrode in zinc-air batteries, the SA-Fe-NHPC demo

241 ctions and cilia and to differentiate at the air-liquid interface like primary cells.

242 imate that up to 87% of PFOS mass was at the air-water interface and less than 4% at the dodecane-wat

243 en bond-driven HIO(3)-IONO(2) complex at the air-water interface undergoes deprotonation and exists a

244 o the gas phase, and we conclude that at the air-water interface, a lower limit for the rate constant

245 the formation of MG diol is catalyzed at the air/liquid water interface compared to the gas phase and

246 e, the solvation and hydrolysis of MG at the air/liquid water interface is studied via classical and

247 re-concentration is directly absorbed by the air (direct air capture) to renew and sustain the carbon

248 e benefits and restrictions of employing the air cathode in superoxide-based batteries.

249 ss concentration is still sufficient for the air quality near airports.

250 bility of dispersal around Antarctica in the air column.

251 were the most dominant ASVs detected in the air in rank order.

252 strategies to maximize spore survival in the air.

253 ularly inflammatory signatures involving the air spaces.

254 taxa of hitchhiking plant propagules on the air-intake grilles of refrigerated shipping containers a

255 passive sensor tags and demonstrate over the air communication of sensor data.

256 In this analysis we quantified the air quality-related public health benefits of the polici

257 Loss rates of NO(2) and O(3) through the air-cleaning system were ~1.5-2.4 h(-1) and ~2.3 h(-1),

258 ntile to the median level of exposure to the air pollutant mixture could occur.

259 nza A viruses that are transmissible via the air preferentially infect ferret and human nasal respira

260 ric acid at the surface of liquid water (the air-water interface).

261 erstanding the drainage dynamics of the thin air film squeezed by gravity between a millimetric dropl

262 Thus, air plasma treatment enables functionalisation of inert

263 cell-derived AT2s that have been adapted to air-liquid interface culture.

264 es overlaid with linseed oil were exposed to air and additional white light.

265 offspring (n = 10/group/sex) were exposed to air or 0.8 ppm ozone for 5 h.

266 Rationale: Exposure to air pollution during intrauterine development and throug

267 large part of students' diurnal exposure to air pollution, especially in cities in developed countri

268 whether pregnancy and childhood exposures to air pollution are related to white matter microstructure

269 ce edge) or inaccessible (solid fast ice) to air-breathing predators.

270 s measured following bolus addition of NO to air-equilibrated cells.

271 CI: 93.2, 179.4) premature deaths related to air pollution, with rural-urban producing the highest ri

272 nction at ages 8 and 15 years in relation to air pollution exposures during pregnancy, infancy, and c

273 he transformation is performed in an open-to-air flask as it shows negligible sensitivity toward air/

274 sk as it shows negligible sensitivity toward air/moisture.

275 nism for globe readings to incorrectly track air temperatures.

276 Here we introduce the concept of "trapped air" metamaterial, fabricated via vat photopolymerizatio

277 1.6; P = 0.003) and Aspergillus with trapped air (difference, 3.2; 95% confidence interval, 1.0-5.4;

278 as Mount Bachelor received free tropospheric air masses on certain nights during the sampling period.

279 However, on typical air pollution events, fire emissions contributed as high

280 producing) photosynthesis in daylight under air.

281 bstrates, and the reaction is operated under air with excellent site-selectivity.

282 65,000 people were exposed to very unhealthy air (daily average PM(2.5) >= 150.5 mug/m(3)).

283 )Po levels and exposure parameters for urban air pollution using linear regression models adjusted fo

284 nding ports are a major contributor to urban air pollution in coastal and inland riverside cities.

285 This study uses air quality modeling and observations over the past four

286 health risk by reducing "business as usual" air pollutant emissions from economic activities.

287 The proposed technique utilizes a variable air cavity, formed between a periodic array and a ground

288 sional changes of wood exposed to a variable air moisture content and potentially reduces wood biodeg

289 The variable air cavity is controlled by means of a piezoelectric act

290 res obtained from the in vitro model (CS vs. air) with a published data set from human epithelial bru

291 combining with its good machine washability, air permeability, flame-retardency, durability, and repe

292 a strong electric field formed at the water-air interface of microdroplets, no catalysts or external

293 The coprimary study outcome measures were air kerma, dose-area product, fluoroscopy time, volume o

294 the world's population living in areas where air quality does not meet current WHO guidelines, combin

295 ially in cities in developed countries where air pollution is caused predominantly by vehicle traffic

296 imary limiting factors to GPP beginning with air temperature in winter and proceeding to moisture and

297 pnea score change correlated positively with air trapping extent change (r(s) = 0.46, P = .001) and e

298 ulfur batteries, lithium-air batteries, zinc-air batteries, and aluminum-air batteries.

299 As the air electrode in zinc-air batteries, the SA-Fe-NHPC demonstrates a large peak

300 The aqueous rechargeable Zn-air batteries assembled with this carbon aerogel exhibit