ライフサイエンスコーパス: air quality

1 arbonaceous materials and impact climate and air quality.

2 ducing greenhouse gas emission and improving air quality.

3 er (PM) with impacts on health, climate, and air quality.

4 ncertainties in our current understanding of air quality.

5 ntervention use, drinking water quality, and air quality.

6 reported ARI despite no evidence of improved air quality.

7 ly in geographical areas suffering from poor air quality.

8 r quantifying aerosol effects on climate and air quality.

9 ts of biogenic SOA on the global climate and air quality.

10 emonstrate the resulting impacts on regional air quality.

11 evidence that the program expansion improved air quality.

12 sure the effect of the Saturday expansion on air quality.

13 ch could further induce feedback on regional air quality.

14 nts to the atmosphere, impacting climate and air quality.

15 t stronger in East Asia due to deteriorating air quality.

16 yields while avoiding substantial impacts on air quality.

17 the important factors that affect the indoor air quality.

18 ve tasks of occupants through measurement of air quality.

19 tagnation episodes, can significantly affect air quality.

20 nce particulate formation, and degrade local air quality.

21 m U.S. oil and natural gas (O&NG) sources on air quality.

22 are not affected by seasonal fluctuations in air quality.

23 rgy budget and/or lead to the degradation of air quality.

24 the BRANN model for spatial interpolation of air quality.

25 f open garbage burning emissions on regional air quality.

26 aerosol lifetime and thus impact climate and air quality.

27 hip between local emission sources and local air quality(2).

28 that O&NG emissions significantly affect the air quality across most of the United States, can region

29 Air quality across the northern hemisphere over the past

30 e investigated the impact of London's LEZ on air quality and children's respiratory health.

31 gas in China has a good chance of delivering air quality and climate cobenefits, particularly when us

32 ome, novel genetic associations with asthma, air quality and climate effects on asthma, exposures dur

33 ion inventories serve as critical inputs for air quality and climate models but are poorly constraine

34 from animal husbandry are important to both air quality and climate, but are hard to characterize an

35 tion of secondary species that impact global air quality and climate, our assessment of ROC abundance

36 pheric particle burden with implications for air quality and climate.

37 spheric hydroxyl radical (OH), which impacts air quality and climate.

38 leading contributor of emissions that affect air quality and climate.

39 ies of trace gases and particles that impact air quality and climate.

40 ctive nitrogen (N), which degrades water and air quality and contributes to climate change.

41 coupled direct method to quantify changes in air quality and epidemiological evidence to determine co

42 boundary layer (PBL) is key for forecasting air quality and estimating greenhouse gas (GHG) emission

43 the impact of coal cookstoves on the ambient air quality and for a more realistic assessment of healt

44 fire emissions and their impacts on regional air quality and global climate.

45 These potential air quality and health cobenefits of biochar use highlig

46 We use regional air quality and health cost models to assess how these s

47 hese soil NO reductions could influence U.S. air quality and health costs.

48 ernational trade on air pollutant emissions, air quality and health have been investigated regionally

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

50 rating unit (EGU) emissions adversely impact air quality and human health by increasing ambient conce

51 We emphasize the dual role of vegetation for air quality and human health in cities during warm seaso

52 s emitted from fossil fuel burning can cause air quality and human health issues.

53 nvironmental epidemiological studies linking air quality and human health.

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

55 (NO(y); NO(y) = NO + NO(2) + HONO) decrease air quality and impact radiative forcing, yet the factor

56 e contributes to degraded indoor and ambient air quality and may affect global surface temperature.

57 Here, we quantify the air quality and mortality impacts of a 12% summertime (J

58 er sector demand and emissions, study of the air quality and public health impacts of EE has been lim

59 uated, intervention aimed at improving urban air quality and public health.

60 ubstantially and quickly to improve in urban air quality and reductions in human exposure.

61 n to GH risk in the Consortium on Safe Labor/Air Quality and Reproductive Health Study (United States

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

63 from internal combustion engines deteriorate air quality and significantly affect human wellbeing and

64 s all think critically about hospital indoor air quality and the approaches to remove, dilute, and di

65 Vegetation and peatland fires cause poor air quality and thousands of premature deaths across den

66 tern China will benefit from improvements in air quality and will facilitate that improvement by prov

67 on Sea Basin in California suffers from poor air quality, and an expanding dry lakebed (playa) presen

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

69 d the fundamental science of the atmosphere, air quality, and diseases diagnostic.

70 opportunities for cities to realize climate, air quality, and health co-benefits through low-carbon d

71 s of the leak on transient weather, climate, air quality, and health in California and the Los Angele

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

73 modeling framework of the economy, climate, air quality, and human health to quantify the effect of

74 , HONO, ...) can negatively impact climate, air quality, and human health.

75 tiscale Air Quality (CMAQ) model to simulate air quality, and the Environmental Benefits Mapping and

76 al emissions affect not only rural but urban air quality, and the impacts are highly seasonal and loc

77 e benefits with respect to exhaust burden on air quality, and thus their utilization should be promot

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

79 candidate for total bioaerosol detection and air quality assessment.

80 e regulations (No Regulations Case) with the air quality associated with current regulations (Regulat

81 s benefits for climate change mitigation and air quality at essentially all decadal to centennial tim

82 nd rural electrification to achieve improved air quality at regional scales, which also has substanti

83 pact of wildland fires on particulate matter air quality at the surface.

84 gional and global scale with large impact on air quality, atmospheric deposition and the radiative fo

85 l network (BRANN) model to predict near-road air quality based on measurements of ultrafine particles

86 2.5 concentrations, indicating an additional air quality benefit under effective pollution control po

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

88 Air quality benefits of electrification are modest, most

89 rtage of natural gas greatly jeopardized the air quality benefits of the coal-to-gas strategy in wint

90 for quantifying their effects on climate and air quality, but its global distribution is poorly chara

91 technologies are having a positive effect on air quality, but persistent air pollution is increasingl

92 ed special focus on the potential to improve air quality by reducing agricultural emissions, which ar

93 to local sources of air pollution, but local air quality can also be affected by atmospheric transpor

94 Air quality can also be affected by distant emission sou

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

96 developed city in the tropical region, where air quality can be influenced by multiple local urban so

97 s study demonstrated the impact that ambient air quality can have on drinking water supplies.

98 to continue facing significant wildfire and air quality challenges with on-going climate change.

99 evidence on the effects of e-cigs on indoor air quality, chemical compositions of mainstream and sec

100 As part of the Research on Emissions Air quality Climate and Cooking Technologies in Northern

101 unds (bVOCs) with potential implications for air quality, climate and human health.

102 ive emission potential due to the impacts on air quality, climate, and biogeochemical cycles.

103 mprove assessment of LSA impacts on regional air quality, climate, and health.

104 c sulfate aerosols have important impacts on air quality, climate, and human and ecosystem health.

105 ere estimated using the Community Multiscale Air Quality (CMAQ) downscaler.

106 ting IEPOX SOA based on Community Multiscale Air Quality (CMAQ) model algorithms and a recently intro

107 The Community Multiscale Air Quality (CMAQ) model has the potential to fill the g

108 tion and emissions, the Community Multiscale Air Quality (CMAQ) model to simulate air quality, and th

109 . is examined using the Community Multiscale Air Quality (CMAQ) model.

110 r Research Forecast and Community Multiscale Air Quality (CMAQ) models.

111 Community Multiscale Air Quality (CMAQ) simulations of a July 2006 ozone poll

112 nested global-through-local weather-climate-air quality computer model.

113 In order to address energy security and air quality concerns, China issued the Dual Credit polic

114 Air quality control is an important task in prevention o

115 atment of VOCs that could be used for indoor air quality control, when coupled with a VOC microconcen

116 tantially reduced FE use, GHG emissions, and air quality damages, without compromising economic or ag

117 Statistical analysis combining air quality data and meteorological data further indicat

118 ble measurement approach could address major air quality data gaps worldwide.

119 of Oakland, CA, developing the largest urban air quality data set of its type.

120 ic content, and discussed in connection with air quality data.

121 particles and their contributions to indoor air quality deterioration were examined by collecting PM

122 air-filter intervention that improved indoor air quality did not affect quality-of-life measures.

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

124 ijing and surrounding regions to ensure good air quality during the 2014 Asia-Pacific Economic Cooper

125 uch as automobile, aerospace, safety, indoor air quality, environmental control, food, industrial pro

126 global scale and their potential impacts on air quality, especially the high pollution episodes.

127 cus on particular contexts, such as water or air quality, fisheries, or land use.

128 ive volatile sensors for medical diagnostic, air quality, food safety and border security application

129 e achieving the desired outcome of improving air quality for the state, particularly in goods movemen

130 These contribute to eutrophication, reduced air quality, global warming, and odor nuisance.

131 s the World Health Organization (WHO) annual air quality guideline (10 ug m(-3)) would remain far off

132 y Standard (NAAQS, 75 mug/m3) or the ambient air quality guideline (AQG) of the World Health Organiza

133 surements exceeded World Health Organization air quality guidelines.

134 ally lasts only a few weeks, while long-term air-quality guidelines are based on annual-averaged conc

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

136 Thus, NOx emission controls to improve ozone air quality have a significant cobenefit in reducing HCH

137 Citizen science projects that monitor air quality have recently drastically expanded in scale.

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

139 The results from this work suggest that the air quality impacts of biomass burning emissions can ext

140 U.S.-wide air quality impacts of electrifying vehicles and off-roa

141 This study examines air quality impacts of scenarios for energy production a

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

143 or modeling future atmospheric chemistry and air quality impacts.

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

145 important contributions to their climate and air quality impacts.

146 ortant implications for estimated health and air quality impacts.

147 We aim to evaluate the air-quality impacts of widespread cool-roof installation

148 assessed the impact of regulatory actions on air quality improvement through a comprehensive monitori

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

150 antification of potential health benefits of air quality improvement.

151 Our estimates imply that air quality improvements over the past 4 decades have st

152 We aimed to assess the potential effects of air-quality improvements on respiratory health by invest

153 Impacts of aviation emissions on air quality in and around residences near airports remai

154 en wind speed and PM2.5 and how it moderates air quality in Beijing, Shanghai, and Xiamen.

155 tified as one of key factors responsible for air quality in Beijing.

156 Here, we compare the impact on air quality in California should California not have ado

157 hensively examines the urban form effects on air quality in cities of different population sizes, at

158 ons from marine traffic affect significantly air quality in coastal areas and the climate.

159 y, the effect of crop residue burning on the air quality in Delhi has not been fully quantified and t

160 ratures and may lead to severe problems with air quality in densely populated areas during heat waves

161 ast, interprovincial trade leads to improved air quality in developed coastal provinces with a net ef

162 r this period, despite small improvements in air quality in highly polluted urban areas during the im

163 ndomized controlled trials to improve indoor air quality in homes of children with asthma are limited

164 ssions are especially critical for the urban air quality in Singapore: fine particular matters (PM(2.

165 xamine the impact of fossil fuel aerosols on air quality in Southeast Asia under five different hypot

166 mortality may help to guide improvements to air quality in the contiguous United States.

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

168 icity reliability networks negatively impact air quality in their own region and in neighboring geogr

169 educing greenhouse gas emissions, to improve air quality in urban centres and to meet the needs of co

170 ta (e.g., surveys, devices, geolocation, and air quality) in a subset of users over the 6-month study

171 ta further indicates strong sensitivities of air quality (including both average air pollutant concen

172 Despite improvement in overall air quality, increased acute air pollution episodes were

173 Sample stratification based on Air Quality Index (AQI) demonstrated that many microbial

174 studied its dynamics relative to daily local air quality index and PM(2.5) concentrations (fine parti

175 to have different sensitivities to SWB when air quality index exceeds approximately 200 AQI.

176 on increase in the PM(2.5) concentration (or Air Quality Index) is associated with a 0.043 (or 0.046)

177 2.5 um) increases to approximately 150 AQI (air quality index).

178 record of location-specific, time-integrated air quality information.

179 nterpretation: Our results suggest that poor air quality is a modifiable risk factor for bone fractur

180 less understood linkage between weather and air quality is the temperature-dependence of emissions f

181 or U.S. urban and industrial area where poor air quality is unevenly distributed and a disproportiona

182 .3 million individuals experienced unhealthy air quality levels for more than 10 days due to smoke.

183 the Southeast, posing challenges to regional air quality management.

184 expected, with implications for exposure and air-quality management in cities that, like St. Louis, a

185 health efforts to reduce smoking and improve air quality may have the added benefit of preventing the

186 Therefore, improvements in air quality may promote molecular longevity from birth o

187 Improving air quality may reduce the future population burden of p

188 Improving air quality may therefore be key to lowering the neonata

189 From analysis of air quality measurement data from the UK and France, we

190 compare well when evaluated against surface air quality measurements.

191 represent potential avenues for climate and air quality mitigation in urban areas.

192 estimated by combining Community Multiscale Air Quality Model (CMAQ) simulations with stationary mon

193 e estimated for 2030 using 3-D photochemical air quality model and detailed emissions inventories.

194 We used the Community Multiscale Air Quality model employing the decoupled direct method

195 Using Community Multiscale Air Quality model estimated PM2.5 total and component co

196 A hybrid air quality model has been developed and applied to esti

197 017 California wildfires, using the Constant Air Quality Model Performance (CAMP) and Bayesian Maximu

198 hemical dispersion model CAMx (Comprehensive Air Quality Model with Extensions), we estimate the bene

199 have been used with the Community Multiscale Air Quality model, simulating the effects of input uncer

200 We applied air quality modeling and health impact assessment tools

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

202 The Community Multiscale Air Quality Modeling System (CMAQ) and Downscaler Model

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

204 emission sources, which benefit both climate/air-quality modeling and mitigation policies in South As

205 accounts for uncertainty by using a range of air quality models (AP3, EASIUR, and InMAP) and concentr

206 Most empirical air quality models (e.g., land use regression) focus on

207 Modified Community Multi-scale Air Quality models estimated air pollution exposures for

208 mation on SO2 sources is a required input to air quality models for pollution prediction and mitigati

209 n was based on modified Community Multiscale Air Quality models.

210 of VOCs and representing them in climate and air quality models.

211 ive techniques for use in parametrization of air quality models.

212 The analysis is based on the assumption that air-quality models adequately describe the dilution proc

213 However, current air-quality models generally underestimate the rate of c

214 This may arise because the air-quality models rely upon kinetics studies of SO(2) o

215 for adequate updating of local and regional air-quality models with the effects of activities of RBS

216 r-based sampling method compatible with both air quality monitoring and Raman spectral imaging (RSI)

217 nonlinear relationship between ground-based air quality monitoring station measurements of PM(2.5),

218 ate estimation of PM(2.5) concentrations for air quality monitoring.

219 chemical vapour remote detection and future air quality monitoring.

220 complies with the EU-quality objectives for air-quality monitoring.

221 g idle emissions could substantially improve air quality near airports.

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

223 A comprehensive investigation using the air quality network and meteorological data of China in

224 The air quality of many large coastal areas in the United St

225 ly draw attention to the rapid deteriorating air quality over Central India, but also underline the s

226 Aircraft-origin UFPs adversely affect air quality over large residential areas downwind of air

227 field burning to mitigate episodic hazardous air quality over northern India.

228 benefits of cool roofs could outweigh small air-quality penalties, UV reflectance standards for cool

229 ion inventories but is of importance from an air quality perspective.

230 erlooked consideration in effective regional air quality planning for China.International and domesti

231 he potential magnitude of health benefits of air quality policies targeting O3, health co-benefits of

232 annually, but will importantly depend on the air quality policies that nations adopt independently of

233 implementation of local, state, and federal air quality policies.

234 al equity-efficiency trade-offs in designing air quality policies.

235 data to be used for compliance checking and air-quality policy use.

236 in using these citizen-derived data sets for air-quality policy.

237 Drought conditions affect ozone air quality, potentially altering multiple terms in the

238 erse ecosystems and fire regimes may improve air quality predictions downwind of wildland fires.

239 ered in chemical transport models to improve air quality predictions.

240 y is a major pollutant contributing to their air quality problems.

241 Since local variation in air quality profoundly impacts public health and environ

242 on fuel that can significantly improve local air quality, reduce greenhouse-gas emissions, and decrea

243 and a chemical transport model, the flexible air quality regional model.

244 gate the sources of WS-Fe and the effects of air quality regulations on ambient levels of WS-Fe.

245 From the 1970s to 1990s, more stringent air quality regulations were implemented across North Am

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

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

248 the previous model by updating emissions and air quality relationships, adding a health impacts modul

249 been extensively studied, their feedback on air quality remains unclear.

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

251 Dense networks of low-cost air quality sensors are emerging to characterize the spa

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

253 Due to the rapid development of low-cost air-quality sensors, a rigorous scientific evaluation ha

254 Using air quality simulated for the period between 2008 and 20

255 A 12-year (2004-2015) regional air quality simulation was conducted over East Asia (27-

256 a region's ability to meet National Ambient Air Quality Standard (NAAQS) obligations for ozone.

257 t PM2.5 has met the Chinese National Ambient Air Quality Standard (NAAQS, 75 mug/m3) or the ambient a

258 n's surface had benzene concentrations above air quality standard of 5 mug/m(3) set by European Union

259 M2.5 levels were measured well below the WHO air quality standard.

260 million people) would meet the Indian annual air-quality standard (40 mug m(-3)) compared with baseli

261 found to exceed Level 2 of the China Ambient Air Quality Standards (CAAQS) enacted in 2012 (>35 mug/m

262 s required to reexamine its National Ambient Air Quality Standards (NAAQS) every 5 years, but evidenc

263 National air quality standards and emission control technologies

264 oring of CO(2) levels to maintain acceptable air quality standards and improve energy efficiency.

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

266 ow us to evaluate strategies to attain ozone air quality standards at minimum cost or to maximize net

267 e environments being noncompliant with legal air quality standards for nitrogen dioxide (NO(2)).

268 critical for estimating this burden, setting air quality standards, and in benefits assessments.

269 sk occurred at levels below current national air quality standards, suggesting that these standards m

270 levels largely below U.S. and European Union air quality standards.

271 evels below the most recent National Ambient Air Quality Standards.

272 nmental Protection Agency's National Ambient Air Quality Standards.

273 iculate matter in an area that often exceeds air quality standards.

274 sing satellite data and a network of >10,000 air quality stations.

275 trate the importance of adopting sustainable air quality strategies in urban planning.

276 ations that need to be taken into account by air quality studies.

277 n and Cu and can play a major role in future air quality studies.

278 A chemical assay widely used in ambient air-quality studies showed that particles from various f

279 om the Environment Protection Agency's Fused Air Quality Surface Using Downscaling tool that integrat

280 PurpleAir low-cost sensors were paired with air quality system (AQS) regulatory stations, and calibr

281 e U.S. Environmental Protection Agency (EPA) Air Quality System and Interagency Monitoring of Protect

282 S. Environmental Protection Agency's (EPA's) Air Quality System matched to residential address, in 1,

283 nd 2014 that Environmental Protection Agency Air Quality System O3 monitors are influenced by smoke.

284 2017, with ground-based monitoring data from air quality system sites, using satellite-based hazard m

285 d from the Environmental Protection Agency's Air Quality System.

286 reduce emissions regionally to meet ambient air quality targets.

287 try in 2013 that aimed at the improvement of air quality: the introduction of the emission trading sy

288 and spatial variations in the sensitivity of air quality to extreme air pollution meteorology.

289 Sensors can measure air quality, traffic congestion, and other aspects of ur

290 age burning and its contribution to regional air quality, using new observational data, a new invento

291 zip-code-level SES (var(SES) = 0.002), daily air quality (var(AQI) = 0.0004), and average temperature

292 en of disease to either population growth or air quality varies regionally and suggests that emission

293 the reduction of emissions through action on air quality, vehicle emissions, and renewable portfolio

294 d strong connections between meteorology and air quality, via chemistry, transport, and natural emiss

295 oor environmental quality, particularly poor air quality, was associated with increased mortality and

296 the effects of distant wildfires on regional air quality were indicated over a several day period in

297 tion affects energy use, climate change, and air quality, when considering farm operations and supply

298 These findings suggest that improving air quality with even lower PM2.5 than currently allowed

299 Men living in neighborhoods with worse air quality-with higher PM2.5 levels and/or temperatures

300 creased incidences of neonatal jaundice when air quality worsens, yet no studies have quantified this