ライフサイエンスコーパス: air quality

1 emonstrate the resulting impacts on regional air quality.

2 tagnation episodes, can significantly affect air quality.

3 cant contributors to poor local and regional air quality.

4 ilation, it will still result in poor indoor air quality.

5 requency and population exposure to degraded air quality.

6 e particles affect Earth's climate and local air quality.

7 res, and rehabilitation), and improvement in air quality.

8 entilation to effectively protect the indoor air quality.

9 gas (UNG) production operations on regional air quality.

10 missions are capable of influencing regional air quality.

11 rn found to be oftentimes worse than outdoor air quality.

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

13 prove to be important to local and regional air quality.

14 the impact of a short-term traffic change on air quality.

15 reduce soil NOx emissions, thereby improving air quality.

16 isen regarding impacts on water supplies and air quality.

17 ancing aerosol emissions with degradation in air quality.

18 ch could further induce feedback on regional air quality.

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

20 evidence that the program expansion improved air quality.

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

22 yields while avoiding substantial impacts on air quality.

23 the important factors that affect the indoor air quality.

24 Air quality across the northern hemisphere over the past

25 usion, wood combustion significantly affects air quality also in areas where it is not the primary he

26 sible, which has implications for studies of air quality and acid deposition.

27 Ship emissions degrade air quality and affect human health, and are increasingl

28 fornia during the California at the Nexus of Air Quality and Climate Change (CalNex) study.

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

30 aerosol-climate feedback mechanisms, and the air quality and climate effects of biogenic emissions ge

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

32 articulate matter has major implications for air quality and climate forcing, but remains uncertain e

33 ult means that the impact of fires on future air quality and climate in Equatorial Asia will be decid

34 ogenic interactions and consequently improve air quality and climate simulations.

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

36 atmospheric particulate matter that affects air quality and climate, remains poorly understood.

37 stion of fossil fuels have strong impacts on air quality and climate, yet quantitative relationships

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

39 portant subject of ongoing research for both air quality and climate.

40 nce of aqSOA from anthropogenic emissions on air quality and climate.

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

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

43 The air quality and fuel consumption impacts were estimated

44 matter with strong implications for regional air quality and global climate change.

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

46 rge source of emissions that impact regional air quality and global climate.

47 Relationships between air quality and health are well-described, but little in

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

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

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

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

52 Further to the direct air quality and health implications of ammonia, this may

53 valuate the impact of climate change on U.S. air quality and health in 2050 and 2100 using a global m

54 s and determine causal relationships between air quality and health.

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

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

57 nvironmental epidemiological studies linking air quality and human health.

58 OA) is well-known to have adverse effects on air quality and human health.

59 ecosystem health in West Africa via improved air quality and increased rainfall.

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

61 We develop a methodology that uses available air quality and meteorological data and simplified fores

62 Here we investigate the impact on air quality and population exposure of wildfires in Equa

63 rios using a single-zone box model of indoor air quality and ratios of thermal efficiency.

64 he southeast U.S. in the context of improved air quality and recently noted reductions in particulate

65 ne among 223,375 singleton deliveries in the Air Quality and Reproductive Health Study (2002-2008).

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

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

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

69 imate change may have detrimental impacts on air quality and, combined with a growing population, may

70 Quantitative simulation of SOA within air-quality and climate models--and its resulting impact

71 ll help improve the representation of SOA in air-quality and climate models.

72 ll-documented detrimental effects on health, air quality, and climate.

73 have a significant effect on global climate, air quality, and consequently human health.

74 ce regulating their impacts on human health, air quality, and direct and indirect radiative forcing o

75 ore significant determination on local-scale air quality, and had improved adaptability between data

76 emission inventories to assess the climate, air quality, and health impacts of natural gas systems.

77 pheric organic aerosols that affect climate, air quality, and health.

78 the tradeoffs between weatherization, indoor air quality, and health.

79 ation, proximity to local sources, area-wide air quality, and meteorological conditions.

80 sing matters of toxicity, exposure pathways, air quality, and water quality.

81 U.S. CO2 emission reduction policies on 2050 air quality are analyzed using the community multiscale

82 Implications for air quality are discussed.

83 ; conversely, NH3 reductions may not improve air quality as much as previously assumed.

84 se questions about the balance of impacts on air quality, as increased emissions from production acti

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

86 on the social costs of pollution assumed, an air quality benefit of $70-150 million per year could be

87 2.5 concentrations, indicating an additional air quality benefit under effective pollution control po

88 A common measure used in air quality benefit-cost assessment is marginal benefit

89 Air quality benefits of electrification are modest, most

90 to coemitted pollutants, the climate-induced air quality benefits of policy increase with time and ar

91 e populations vary greatly, we simulated the air quality benefits of scenarios reflecting no action,

92 n examination of the potential emissions and air quality benefits of shifting freight from truck to r

93 tribution to CH4 abatement, with climate and air quality benefits.

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

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

96 d strongest anthropogenic greenhouse gas and air quality by influencing tropospheric ozone levels.

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

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

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

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

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

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

103 mospheric environment and climate, impacting air quality, cloud formation, and the Earth's radiation

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

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

106 The adjoint of the Community Multiscale Air Quality (CMAQ) model at 1 km horizontal resolution i

107 heating fuels using the Community MultiScale Air Quality (CMAQ) model conducted at a high spatial res

108 sion scenarios with the Community Multiscale Air Quality (CMAQ) model during the July 2006 heat wave.

109 tal Protection Agency's community multiscale air quality (CMAQ) model routinely underpredicts peak oz

110 We apply the Community Multiscale Air Quality (CMAQ) model to a domain covering the easter

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

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

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

114 ggressive carbon tax leads to improved PM2.5 air quality compared to the reference case as incentives

115 is less than 1% higher in the scenarios with air quality compliance costs than in scenarios without s

116 t exposure of 69 million people to unhealthy air quality conditions.

117 00% removal of PM2.5 under extreme hazardous air-quality conditions (PM2.5 mass concentration >250 mu

118 fornia, as a result of the implementation of air quality-control policies.

119 his paper compares three scenarios: one with air quality costs included, one without air quality cost

120 with air quality costs included, one without air quality costs, and one in which conversion facilitie

121 regional and global improvements in ambient air quality could reduce attributable mortality from PM2

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

123 Using regional traffic and ambient air quality data from Southern California, we examine th

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

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

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

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

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

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

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

131 ce submicrometer exhaust particles affecting air quality, especially in urban environments.

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

133 on for EGUs in the Eastern U.S. and estimate air quality for four emission scenarios with the Communi

134 vements should be targeted, enhancing indoor air quality for millions of the world's most vulnerable

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

136 surements exceeded World Health Organization air quality guidelines.

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

138 lp inform strategies to monitor and mitigate air quality impacts and provide broader insight into the

139 Air quality impacts are associated with emissions of nit

140 However, our results indicate that the air quality impacts of climate change are substantial an

141 The combined emissions and air quality impacts of electricity generation in the Tex

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

143 A detailed understanding of the climate and air quality impacts of mobile-source emissions requires

144 current understanding of local and regional air quality impacts of natural gas extraction, productio

145 o address community concerns regarding local air quality impacts related to proximate sources, to pro

146 important contributions to their climate and air quality impacts.

147 ortant implications for estimated health and air quality impacts.

148 o-exposure for wildfires and emphasizes that air-quality impacts are not only localized to communitie

149 We evaluated air-quality impacts of PM2.5 from smoke from the Rim Fir

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

151 We employed two approaches to examine the air-quality impacts: (1) an evaluation of PM2.5 concentr

152 .3% to 3.6% across the three periods, as the air quality improved (P = 0.001).

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

154 Our risk model estimates that these air quality improvements decreased the risk of premature

155 economic benefit, with health benefits from air quality improvements potentially offsetting the cost

156 -usage scenarios for achieving modest indoor air quality improvements.

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

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

159 n by moulds, or for the evaluation of indoor air quality in buildings.

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

163 An initial study of air quality in Mecca and surrounding holy sites during t

164 gen oxides (NOx) produces ozone and degrades air quality in polluted regions.

165 diation are needed, because measuring indoor air quality in privately owned buildings is often logist

166 iscoloration is in some way linked with poor air quality in the Agra region, the specific components

167 mit particulate matter (PM) that affects the air quality in the vicinity of airports and contributes

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

169 nversion affecting urban air circulation and air quality in UCL and UBL.

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

173 idative stress in relation to a governmental air quality intervention implemented during the 2008 Bei

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

175 Indoor air quality is an important predictor of health, especia

176 d to air pollution, notably in regions where air quality is not monitored, and also because the toxic

177 On high electricity demand days, when air quality is often poor, regional transmission organiz

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

179 e back' in response to these improvements in air quality is uncertain, with a suggestion that long-te

180 .3 million individuals experienced unhealthy air quality levels for more than 10 days due to smoke.

181 cancer risk through both tobacco control and air quality management may exceed expectations based on

182 tailed PM2.5 concentration patterns can help air quality management plan to meet air quality standard

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

184 ntation in models is important for effective air quality management.

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

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

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

188 expenditure and maintenance, of an extensive air-quality measurement network, we present simple stati

189 compare well when evaluated against surface air quality measurements.

190 pitalization rate, influenza prevalence, and air quality measures are available, but common cold circ

191 estimated by combining Community Multiscale Air Quality model (CMAQ) simulations with measurements f

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

193 was incorporated in the Community Multiscale Air Quality Model (CMAQ) to quantitatively determine con

194 ncentrations using the community multi-scale air quality model (CMAQ).

195 are analyzed using the community multiscale air quality model (CMAQ).

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

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

198 s of exposure error: deltaspatial (comparing air quality model estimates to central-site measurements

199 aring population exposure model estimates to air quality model estimates), and deltatotal (comparing

200 exposure metrics (central-site measurements, air quality model estimates, and population exposure mod

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

202 re linked with modified Community Multiscale Air Quality model outputs.

203 nly in contrast with the RAMP and a Constant Air Quality Model Performance (CAMP) scenarios.

204 l scale, we introduce our novel Regionalized Air Quality Model Performance (RAMP) approach to integra

205 ly 2030 in the U.S., using the Comprehensive Air Quality Model with Extensions and assuming advanced

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

207 Based on the indoor air quality model, there are multiple performance-usage

208 t sensitivity analysis in a state-of-the-art air quality model, we estimate MBs for NOx emitted from

209 with accuracy comparable to a comprehensive air quality model.

210 stically evaluate the results of a numerical air quality model.

211 from monitor-corrected Community Multi-Scale Air Quality modeling data.

212 from monitor-corrected Community Multi-Scale Air Quality modeling data.

213 Integrated power system and air quality modeling methods were developed to evaluate

214 Furthermore, the Real-time Air Quality Modeling System (RAQMS) analyses indicate th

215 Integrating accurate air quality modeling with decision making is hampered by

216 Understanding these emissions may improve air quality modelling as NOx contributes to formation of

217 Current air quality models are not well suited to evaluate the i

218 es monitoring data and outputs from existing air quality models based on Land Use Regression (LUR) an

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

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

221 Underprediction of peak ambient pollution by air quality models hinders development of effective stra

222 rocedure eliminates the need to rely only on air quality models to generate dilution factors.

223 Modified Community Multiscale Air Quality models were used to estimate mean exposures

224 represented in 3D atmospheric chemistry and air quality models.

225 source of uncertainty in global climate and air quality models.

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

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

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

229 ntial mobility spectrometry (GC-DMS) via the Air Quality Monitor (AQM), while water is analyzed to me

230 cal center who lived less than 50 km from an air quality monitor and had an ARDS risk factor.

231 ram enrollment data, DR event records, ozone air quality monitoring data, and emission characteristic

232 nique, thus greatly improving performance of air quality monitoring devices.

233 lar and pulmonary diseases, but conventional air quality monitoring gives no information about biolog

234 rom the U.S. Environmental Protection Agency air quality monitoring network and daily emergency hospi

235 nd economically to extend the coverage of an air quality monitoring network.

236 sing annual averages of NOx at all available air quality monitoring sites in Israel between 1991 and

237 Association (WBEA) at four community ambient Air quality Monitoring Stations (AMS) in the Athabasca O

238 ly that reducing these emissions may improve air quality more now than they would have in 2005; conve

239 LAX emissions adversely impacted air quality much farther than reported in previous airpo

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

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

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

243 spite attempts and some successes to improve air quality over the decades, current US national trends

244 result has important implications for indoor air quality, particularly given the current trend for gr

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

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

247 Air quality planning that capitalizes on a priori knowle

248 stern Texas for a high ozone episode used in air quality planning.

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

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

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

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

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

254 While air quality regulation may substantially affect local de

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

256 nd building materials and are the subject of air quality regulations.

257 We evaluate the air quality-related human health impacts of 10 such opti

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

259 roving the characterization of emissions and air quality responses to the intervention.

260 nits" are exempt from some federal and state air quality rules.

261 -iron pipes will improve consumer safety and air quality, save money, and lower greenhouse gas emissi

262 ed particulate nitrate in future climate and air quality scenarios may be under predicted because the

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

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

265 for use as a biofuel feedstock will have on air quality, specifically ground-level ozone concentrati

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

267 for effective implementation of the US ozone air quality standard.

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

269 ttainment area for the U.S. National Ambient Air Quality Standards (NAAQS).

270 National air quality standards and emission control technologies

271 s than the reduction of the National Ambient Air Quality Standards for PM2.5 from 15 to 12 mug m(-3).

272 can help air quality management plan to meet air quality standards more effectively.

273 zone mixing ratios well in excess of present air quality standards, but only during winter.

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

275 d attention due to the tightening of ambient air quality standards.

276 face multiple challenges in meeting federal air quality standards.

277 ual Environmental Protection Agency National Air Quality Standards.

278 n the 2008 review of the Pb national ambient air quality standards.

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

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

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

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

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

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

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

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

287 was assigned using data from the U.S. EPA's Air Quality System.

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

289 t areas, which exceed thresholds for healthy air quality, to additional costs.

290 hen assessing long-term emission and ambient air quality trends.

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

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

293 To predict their net effect on regional air quality, we review the emissions literature and deve

294 onships among LULC, ambient temperature, and air quality were analyzed and found to be significant in

295 We found that long-term improvements in air quality were associated with statistically and clini

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

297 he impact of alternative bus technologies on air quality, which was then related to premature mortali

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 In contrast, major improvements in air quality would be required to substantially reduce mo