ライフサイエンスコーパス: particulate matter

1 ion and corresponding ground-level ozone and particulate matter.

2 ection Agency (EPA), not including ozone and particulate matter.

3 imate the annual mean concentrations of fine particulate matter.

4 osol (SSA) is a globally important source of particulate matter.

5 crometer-sized objects, such as bacteria and particulate matter.

6 f passive samplers for measuring atmospheric particulate matter.

7 ifers and even less about the attenuation of particulate matter.

8 nsumer products as well as ambient suspended particulate matter.

9 secondary pollutants such as ozone and some particulate matter.

10 a comprehensive understanding of atmospheric particulate matter.

11 ew" particle formation), and complexation to particulate matter.

12 e an important source of organic atmospheric particulate matter.

13 smoke, including those associated with fine particulate matter.

14 of other common pollutants such as ozone and particulate matter.

15 ors, including but not limited to, ultrafine particulate matters.

16 ff-road sector and (b) an increase in PM2.5 (particulate matter 2.5 mum or less in diameter) emission

17 Fine particulate air pollution (PM2.5; particulate matter 2.5 mum or less in diameter) is thoug

18 evel, neighborhood-level, and air pollution [Particulate Matter, 2.5 micrometers or less (PM2.5) and

19 e-range increase in average exposure to fine particulate matter (3.2 microg/m(3)) during pregnancy wa

20 ternal exposure to nitrogen dioxide and fine particulate matter (aerodynamic diameter </=2.5 microm)

21 WO), the role of early life exposure to fine particulate matter (aerodynamic diameter <2.5 mum; PM2.5

22 natal exposure to ambient PM2.5, (i.e., fine particulate matter, aerodynamic diameter </= 2.5 mum) ha

23 Ambient particulate matter air pollution exposure and mortality

24 and to study the impact of wildland fires on particulate matter air quality at the surface.

25 ng-lived surface bound radicals that form on particulate matter and combustion borne particulates, su

26 Associations between source-specific fine particulate matter and emergency department visits for r

27 Air pollution particulate matter and engineered nanomaterials are enco

28 he SWI are sedimentation and resuspension of particulate matter and fluxes of dissolved materials.

29 ompounds are a significant component of fine particulate matter and haze in national parks and wilder

30 Long-term exposure to ambient fine particulate matter and renal function in older men: the

31 rk has examined the association between fine particulate matter and risk of kidney disease; however,

32 resulting from nutrient gradients, suspended particulate matter and stratification.

33 Using colocated observations of particulate matter and the National Weather Service Haza

34 nderstanding differences in EPFR presence on particulate matter and uncover the possibility of remedi

35 een short-term exposure to nitrogen dioxide, particulate matter, and sulfur dioxide and completed sui

36 fied both outdoor air pollution and airborne particulate matter as carcinogenic to humans (Group 1) f

37 than porous aquifers, with the transport of particulate matter being an important factor, little is

38 serve as a major indoor source of biological particulate matter (bioPM).

39 ents can result in significant discharges of particulate matter-bound polycyclic aromatic hydrocarbon

40 re not only phagocytose inhaled microbes and particulate matter but are also crucial in catabolizing

41 PCBs were always mainly associated with particulate matter, but partitioning within different pa

42 icochemical properties of released lifecycle particulate matter (called LCPM) from thermal decomposit

43 res to filtered air and concentrated ambient particulate matter (CAP; mean, 253 +/- 16 mug/m3).

44 Environments) network has characterized fine particulate matter composition at locations throughout t

45 The 2003 annual average fine particulate matter concentration was not associated with

46 statistical model to represent bias of fine particulate matter concentrations (PM2.5) derived from a

47 We calculate that high particulate matter concentrations from fires during Fall

48 cive to the formation of peak ozone and fine particulate matter concentrations.

49 s woodland had the greatest stocks of coarse particulate matter (CPOM) and greater numbers of 'shredd

50 The Network is currently producing real-time particulate matter data from 40 low-cost sensors through

51 nfidence interval (CI): 1.04, 1.39) and fine particulate matter (diameter </=2.5 mum) on lag day 2 (d

52 Particulate matter dominates the HTI for both systems, r

53 Of these seven, diesel particulate matter (DPM) is the most important; however

54 and toxicological characteristics of diesel particulate matter (DPM).

55 Inhalation of traffic-related particulate matter (e.g., diesel exhaust particles [DEPs

56 d combustion efficiency (MCE) and decreasing particulate matter emission factors (EF).

57 stigated, using wind tunnel experiments, the particulate matter emission potential of a sand and two

58 he impact of gasoline particulate filters on particulate-matter emission, the results for the stock-G

59 s suspended nanoscale cerium oxide to reduce particulate matter emissions and increase fuel economy,

60 is used as a diesel fuel additive to reduce particulate matter emissions and increase fuel economy,

61 Particulate matter emissions from agricultural livestock

62 Particulate matter exposure and cardiopulmonary differen

63 Particulate matter exposure and preterm birth: estimates

64 ge, race/ethnicity, education, prenatal fine particulate matter exposure, prenatal smoking exposure,

65 We used weekly fine-particulate-matter exposure data for 238 births in a bir

66 duration of exposure to fire-originated fine particulate matter (fire-PM2.5) and CHVI.

67 iver Estuary water daily, removing 160 kg of particulate matter from the water column, of which 12 kg

68 s focussed primarily on exhaust emissions of particulate matter from traffic as a causal factor.

69 Nanoscale particulate matter from urban traffic rapidly induces ox

70 anthropogenic emissions to produce ozone and particulate matter has long been recognized.

71 ependence of light absorption by atmospheric particulate matter has major implications for air qualit

72 Many studies have found associations between particulate matter having an aerodynamic diameter of </=

73 gases such as methane and the production of particulate matter important for climate and human healt

74 d to fill the need for more detailed data on particulate matter in an area that often exceeds air qua

75 st particles (DEPs) are a major component of particulate matter in Europe's largest cities, and epide

76 An in vitro phantom model demonstrates that particulate matter in suspension can generate similar OC

77 alumina surfaces, corroborating the role of particulate matter in the cooling down zone of combustio

78 leads to a trapping and massive increase of particulate matter in the near-surface air to which peop

79 iod (OR = 1.35, 95% CI: 1.09, 1.66) and fine particulate matter in the spring (OR = 1.28, 95% CI: 1.0

80 n divided into two groups: (1) dissolved and particulate matter in the wash solutions and (2) the fra

81 The catalytic nature of particulate matter is often advocated to explain its abi

82 Atmospheric particulate matter is one of the main factors governing

83 and it is a major contributor to atmospheric particulate matter known to have a deleterious respirato

84 dels were used to estimate mean exposures to particulate matter less than 10 microm or less than 2.5

85 2, particulate matter less than 2.5 mum, and particulate matter less than 10 mum were not associated

86 n risk associated with exposure to ozone and particulate matter less than 2.5 microm in aerodynamic d

87 ower plants were exposed to higher levels of particulate matter less than 2.5 microm in diameter comp

88 Prenatal exposure to particulate matter less than 2.5 microm in diameter for

89 Long-term exposure to fine particulate matter less than 2.5 mum in diameter (PM2.5)

90 SO2, particulate matter less than 2.5 mum, and particulate ma

91 5 microm in aerodynamic diameter (PM2.5) and particulate matter less than or equal to 10 microm in ae

92 We assessed sex-specific associations of particulate matter less than or equal to 10 mum in diame

93 Particulate matter less than or equal to 2.5 microm in a

94 A 5 mug/m(3) increase in average lifetime particulate matter less than or equal to 2.5 mum in diam

95 one, NO2, SO2, particulate matter < 2.5 mum, particulate matter < 10 mum) were assessed by weighted a

96 ies to determine whether local PM2.5 levels (particulate matter < 2.5 mum in aerodynamic diameter) af

97 Pollutant exposures (ozone, NO2, SO2, particulate matter < 2.5 mum, particulate matter < 10 mu

98 least partly mediated by physical activity, particulate matter < 2.5 mum, social engagement, and dep

99 We use observed values for particulate matter </= 2.5 microns (PM2.5) for this coho

100 cal emissions, to develop the instrument for particulate matter </= 2.5 mum (PM2.5), black carbon (BC

101 isease (CHD) mortality from ambient regional particulate matter </= 2.5 mum (PM2.5).

102 ssociation between prenatal exposure to fine particulate matter </= 2.5 mum in aerodynamic diameter (

103 a positive association between ambient fine particulate matter </= 2.5 mum in aerodynamic diameter (

104 uated associations between concentrations of particulate matter </= 2.5 mum in diameter (PM2.5) and e

105 Studies of prenatal exposure have associated particulate matter </= 2.5 mum in diameter (PM2.5) and o

106 nt (ED) visits and ambient concentrations of particulate matter </= 2.5 mum in diameter (PM2.5) have

107 exposure, using measures of personal PM2.5 (particulate matter </= 2.5 mum) and elemental carbon (EC

108 PM2.5 (particulate matter </= 2.5 mum) has been associated with

109 Long-term exposure to fine particles (particulate matter </= 2.5 mum; PM2.5) has been consiste

110 ns of particulate matter </=2.5 mum (PM2.5), particulate matter </=10 mum (PM10), nitrogen dioxide (N

111 We examined five pollutants (particulate matter </=10 mum and </=2.5 mum in diameter,

112 to determine the recorded concentrations of particulate matter </=2.5 mum (PM2.5), particulate matte

113 ng during pregnancy; season of birth; PM2.5 (particulate matter </=2.5mm in aerodynamic diameter); br

114 xposure was assessed as week-average ambient particulate matter <10 mum in diameter and ammonia (NH3)

115 Week-average particulate matter <10 mum in diameter and NH3 levels we

116 Elevated levels of fine particulate matter <2.5 microm in aerodynamic diameter (

117 Both short- and long-term exposures to fine particulate matter (</= 2.5 mum; PM2.5) are associated w

118 Outdoor fine particulate matter (</= 2.5 mum; PM2.5) has been identif

119 Given that fine particulate matter (</= 2.5 mum; PM2.5) is a mixture of

120 ellite-based nitrogen dioxide (NO2) and fine particulate matter (</= 2.5 mum; PM2.5) predictions at p

121 Ambient particulate matter may upset redox homeostasis, leading

122 Ambient fine particulate matter, nitrogen dioxide, and preterm birth

123 nified modeling approach for predicting fine particulate matter, nitrogen dioxide, oxides of nitrogen

124 Neither particulate matter nor ozone was an important predictor,

125 sized subfraction of urban traffic ultrafine particulate matter (nPM, < 200 nm) in vivo, ex vivo, and

126 r (SN) and mass concentration of nonvolatile particulate matter (nvPM) in the exhaust of a gas turbin

127 ll participants, a 7.9 mug/m(3) increment in particulate matter of <10 mum was associated with higher

128 The effects of particulate matter on human health are well established

129 ry impact of inhaled in situ burned oil sail particulate matter (OSPM).

130 sulfate (nss-SO4(2-)) aerosols and secondary particulate matter over oceans and thus, significantly i

131 tual covariates, including exposures to fine particulate matter, ozone, and nitrogen dioxide.

132 Coarse particulate matter (P10-2.5) is primarily mechanically g

133 Annual averages of fine particulate matter (particles with a mass median aerodyn

134 gated the short-term effects of UFP and fine particulate matter (particulate matter with an aerodynam

135 Estimates of fine particulate matter (particulate matter with an aerodynam

136 fects associated with acute exposure to fine particulate matter (particulate matter with an aerodynam

137 The impact of chronic exposure to fine particulate matter (particulate matter with an aerodynam

138 r energy access solutions in climate change, particulate matter, photochemical oxidants, and terrestr

139 g-term residential concentrations of ambient particulate matter (PM) < 10 mum in diameter (PM10) and

140 ng Particulate Matter (TRANSPHORM) projects: particulate matter (PM) </=2.5mum, </=10mum, and 2.5-10m

141 tility in response to methacholine (MCh) and particulate matter (PM) air pollutants, in the absence o

142 Industrial particulate matter (PM) air pollution exposing nearby re

143 Ambient particulate matter (PM) air pollution exposure has been

144 Whether exposure to ambient air pollution particulate matter (PM) alters protective human host imm

145 The composition of ambient particulate matter (PM) and its sources were investigate

146 onents of air pollution, including gases and particulate matter (PM) by size fraction, chemical compo

147 Ambient particulate matter (PM) can cause adverse health effects

148 Soluble transition metals in particulate matter (PM) can generate reactive oxygen spe

149 ability of Zn and Cu isotopes in atmospheric particulate matter (PM) collected in two major European

150 Particulate matter (PM) concentration data and turbulenc

151 Recent changes of surface particulate matter (PM) concentration in the Seoul Metro

152 During each walk session, black carbon, particulate matter (PM) concentrations, ultrafine partic

153 stigate whether different types of near-road particulate matter (PM) contribute to exacerbation of al

154 Particulate matter (PM) deposited on Platanus acerifolia

155 sociated microbes are aerially dispersed via particulate matter (PM) derived from large-scale beef ca

156 l oxidation catalyst (DOC) on the engine-out particulate matter (PM) emissions morphology and structu

157 ns were posed whether nitric oxide (NOx) and particulate matter (PM) emissions were the same for the

158 Exposure to atmospheric particulate matter (PM) exacerbates respiratory and card

159 Ambient particulate matter (PM) exposure is associated with athe

160 Particulate matter (PM) exposure may directly affect the

161 Traffic-related particulate matter (PM) has been linked to a heightened

162 m BTM generators could also form near-source particulate matter (PM) hotspots.

163 However, BC and particulate matter (PM) household emissions are not well

164 Particulate matter (PM) in atmospheric pollution contain

165 drogen peroxide (H2O2)] catalyzed by ambient particulate matter (PM) in the dithiothreitol (DTT) assa

166 Exposure to ambient particulate matter (PM) induces endothelial dysfunction,

167 Sustained exposure to ambient particulate matter (PM) is a global cause of mortality.

168 Air particulate matter (PM) is a ubiquitous environmental ex

169 H) and oxy-(OPAH)), organic carbon (OC), and particulate matter (PM) less than 2.5 mum in diameter (P

170 at simulate a range of expected tropospheric particulate matter (PM) lifetimes, in order to link thei

171 , GDIs had, on average, a factor of 2 higher particulate matter (PM) mass emissions than PFIs due to

172 However, knowledge of PAH accessibility in particulate matter (PM) of urban origin that may ultimat

173 f adverse health outcomes, and the effect of particulate matter (PM) on the brain is beginning to be

174 icator of airway hyperreactivity) and indoor particulate matter (PM) PM2.5.

175 Particulate matter (PM) pollution has raised serious con

176 Atmospheric particulate matter (PM) samples were collected from four

177 Aircraft engines emit particulate matter (PM) that affects the air quality in

178 In this study, airborne particulate matter (PM) was measured at various location

179 sess the association of prenatal exposure to particulate matter (PM) with newborn telomere length as

180 x), hydrocarbons (HC), carbon monoxide (CO), particulate matter (PM), and carbon dioxide (CO2) emissi

181 th effects following exposure to ambient air particulate matter (PM), and there is strong support for

182 Emissions of particulate matter (PM), carbon monoxide (CO), nitrogen

183 Carbonaceous particulate matter (PM), comprising black carbon (BC), p

184 rsenic species known to exist in atmospheric particulate matter (PM), i.e., the inorganic arsenite iA

185 eleterious health effects of vehicle-emitted particulate matter (PM), including PM2.5 (aerodynamic di

186 cal conditions as potential modifiers of the particulate matter (PM)-mortality association.

187 bon monoxide (CO), carbon dioxide (CO2), and particulate matter (PM).

188 rganic polymers) and inorganic phases of the particulate matter (PM).

189 e and reduce harmful emissions, specifically particulate matter (PM).

190 e atmosphere as mixtures attached to ambient particulate matter (PM).

191 proposed as a measure of toxicity of ambient particulate matter (PM).

192 s pollutants, including combustion-generated particulate matter (PM).

193 (SOA) constitute a large portion of ambient particulate matter (PM).

194 rticles on the nano- and micrometer scale as particulate matter (PM).] However, the experimental resu

195 ioxide, sulfur dioxide, carbon monoxide, and particulate matter (PM10 and PM2.5) were estimated in th

196 r, and I determination in airborne inhalable particulate matter (PM10) collected in the metropolitan

197 ever, the association between ambient coarse particulate matter (PM10; </=10 mum in aerodynamic diame

198 Pollutants measured included PM2.5 (PM = particulate matter), PM10, ultrafine particles, black ca

199 Fine particulate matter (PM2.5) air pollution exposure has be

200 h changes in nitrogen dioxide (NO2) and fine particulate matter (PM2.5) air pollution.

201 Measurements of fine particulate matter (PM2.5) and absorbance were conducted

202 2013, we measured personal exposures to fine particulate matter (PM2.5) and carbon monoxide (CO) over

203 relative to baseline of 45% and 47% for fine particulate matter (PM2.5) and carbon monoxide (CO), res

204 Data on exposures to fine particulate matter (PM2.5) and ozone (O3) were obtained

205 by increasing ambient concentrations of fine particulate matter (PM2.5) and ozone (O3).

206 between short-term exposures to ambient fine particulate matter (PM2.5) and ozone, and at levels belo

207 Vehicle emissions contribute to fine particulate matter (PM2.5) and tropospheric ozone air po

208 h December 2011 and annual estimates of fine particulate matter (PM2.5) by census tract.

209 Exposure to ozone and fine particulate matter (PM2.5) can cause adverse health effe

210 Short-term exposure to ambient fine particulate matter (PM2.5) concentrations has been assoc

211 We estimated global fine particulate matter (PM2.5) concentrations using informat

212 In highly polluted environments, fine particulate matter (PM2.5) containing redox-active trans

213 ould increase ambient concentrations of fine particulate matter (PM2.5) due to its ammonia emissions.

214 l studies associate inhalation of fine-sized particulate matter (PM2.5) during pregnancy with preterm

215 d and analyzed within-city variation of fine particulate matter (PM2.5) elements.

216 Long-term fine particulate matter (PM2.5) exposure is linked with cardi

217 Exposure to fine particulate matter (PM2.5) from indoor and outdoor sourc

218 ion, up to 11 mug m(-3) for annual mean fine particulate matter (PM2.5) in northern Vietnam and up to

219 e suggests that exposure to ambient air fine particulate matter (PM2.5) increases the risk of develop

220 n of DICE-Africa to annual mean surface fine particulate matter (PM2.5) is >5 mug m(-3) in populous N

221 Ambient fine particulate matter (PM2.5) is among the most prevalent s

222 It is unknown if ambient fine particulate matter (PM2.5) is associated with lower rena

223 ing whether chronic exposure to ambient fine particulate matter (PM2.5) is associated with mortality.

224 Inhalation of traffic-associated atmospheric particulate matter (PM2.5) is recognized as a significan

225 Fine particulate matter (PM2.5) is thought to be responsible

226 e system provides nondestructive analysis of particulate matter (PM2.5) mass concentration.

227 can significantly impact ozone (O3) and fine particulate matter (PM2.5) pollution across the U.S. and

228 estimate premature mortality caused by fine particulate matter (PM2.5) pollution as a result of atmo

229 r (April-September) surface ozone (O3), fine particulate matter (PM2.5), and maximum temperature (TX)

230 n 1 ppb for ozone and 0.5 mug m(-3) for fine particulate matter (PM2.5), but widespread.

231 ubstantial mass fraction to atmospheric fine particulate matter (PM2.5).

232 ack carbon (BC), NO, NO2, NOx, SO2, and fine particulate matter (PM2.5)] decreased with increasing wi

233 We examined associations of particulate matter (PM2.5, PM10) and nitrogen oxides (NO

234 dies have provided strong evidence that fine particulate matter (PM2.5; aerodynamic diameter </= 2.5

235 mal chow or a high-fat diet to airborne fine particulate matters (PM2.5), and then investigated the c

236 efficient air filters for removing airborne particulate matters (PMs).

237 time could enhance the probability of severe particulate matter pollution by more than a factor of tw

238 The Salt Lake Valley experiences severe fine particulate matter pollution episodes in winter during p

239 eres are ubiquitous and abundant in airborne particulate matter pollution.

240 China, many regions are subjected to severe particulate matter pollution.

241 g aimed at reducing ozone concentrations had particulate matter reduction co-benefits, but if particu

242 iculate matter reduction co-benefits, but if particulate matter reductions are the primary objective,

243 pecies (ROS) is a hypothesized mechanism for particulate-matter related health effects.

244 trogen dioxide attenuated the full-pregnancy-particulate matter relationship.

245 s associated with seven distinct (suspended) particulate matter samples collected from different urba

246 findings suggest that (1) the pH of ambient particulate matter samples should be measured or control

247 Exposing human lung cells to particulate matter smaller than 10 microm (PM10), signif

248 on spectra of water-soluble BrC from ambient particulate matter smaller than 2.5 mum collected in Ath

249 past studies of archaeal lipids in suspended particulate matter (SPM) and sediments mainly focused on

250 positively correlated primarily to suspended particulate matter (SPM) at sites in areas with a high l

251 st loss and increases in estuarial suspended particulate matter (SPM) concentration.

252 Suspended particulate matter (SPM) is present in the natural aquat

253 The fraction of TMPP sorbed to suspended particulate matter (SPM) was 56.4% of the total mass in

254 primary effluent, final effluent, suspended particulate matter (SPM), and sludge collected from two

255 Humic-like substances (HULIS) in particulate matter such as biomass burning aerosol chela

256 Particulate matter such as black carbon is one of the ma

257 ation, an important component of atmospheric particulate matter that affects air quality and climate,

258 This bias arose from seasonal trends in particulate matter that induced correlation between TAEs

259 cts - Integrated Methodologies for Assessing Particulate Matter (TRANSPHORM) projects: particulate ma

260 ablation, atomization, and excitation of the particulate matter using the rf-GD.

261 measurements of ultraviolet light-absorbing particulate matter (UVPM) in comparison to black carbon

262 pollution measurements (nitrogen oxides and particulate matter) were combined with data from permane

263 These pollutants can be adsorbed to particulate matter which is present in the air or deposi

264 We pooled estimates by pollutant type (particulate matter with a diameter of <2.5 mum [PM2.5] o

265 e long-term health impacts of ozone and fine particulate matter with a diameter smaller than 2.5 micr

266 f life, lifetime, and prior-year exposure to particulate matter with a diameter smaller than 2.5 mum

267 Ambient PM2.5 (particulate matter with aerodynamic diameter </= 2.5 mum

268 (NO2), sulfur dioxide (SO2), ozone (O3), and particulate matter with aerodynamic diameter </= 2.5 mum

269 ere have examined the health effects of PM1 (particulate matter with aerodynamic diameter <1 mum), wh

270 concentrations of nitrogen dioxide (NO2) and particulate matter with aerodynamic diameter <2.5 (PM2.5

271 er <1 mum), which are a major part of PM2.5 (particulate matter with aerodynamic diameter <2.5 mum) a

272 Modeled estimates of particulate matter with aerodynamic diameter <2.5microm

273 n noise (Lden), air pollution [black carbon, particulate matter with aerodynamic diameter <2.5mum (PM

274 eeze and shortness of breath and annual mean particulate matter with aerodynamic diameter <2.5mum, 2.

275 al, rather than traffic-related, exposure to particulate matter with aerodynamic diameter of 2.5 micr

276 weeks of pregnancy, PTB risk associated with particulate matter with aerodynamic diameter of less tha

277 is of the interaction of maternal asthma and particulate matter with aerodynamic diameter of less tha

278 ynamic diameter of less than 2.5 microns and particulate matter with aerodynamic diameter of less tha

279 tion associated with short-term exposures to particulate matter with an aerodynamic diameter < 2.5 mu

280 lanced order to diesel exhaust (200 mug/m(3) particulate matter with an aerodynamic diameter </= 2.5

281 Daily concentrations of particulate matter with an aerodynamic diameter </=2.5 m

282 ith an aerodynamic diameter <2.5 mum, 7% for particulate matter with an aerodynamic diameter <10 mum,

283 weeks 1-20, 17% for nitrogen oxides, 10% for particulate matter with an aerodynamic diameter <2.5 mum

284 We investigated the impact of particulate matter with an aerodynamic diameter less tha

285 rm associations of air pollution, defined as particulate matter with an aerodynamic diameter less tha

286 effects of UFP and fine particulate matter (particulate matter with an aerodynamic diameter less tha

287 h acute exposure to fine particulate matter (particulate matter with an aerodynamic diameter less tha

288 , we found that a 10-microg/m(3) increase in particulate matter with an aerodynamic diameter less tha

289 e-, 2-, and 5-year average concentrations of particulate matter with an aerodynamic diameter less tha

290 chronic exposure to fine particulate matter (particulate matter with an aerodynamic diameter less tha

291 ic were estimated (nitrogen oxides [NOx] and particulate matter with an aerodynamic diameter of <10 m

292 mated using annual average concentrations of particulate matter with an aerodynamic diameter of 2.5 m

293 Health impacts owing to changes in ambient particulate matter with an aerodynamic diameter of 2.5 m

294 associations between coexposure to prenatal particulate matter with an aerodynamic diameter of less

295 e concentrations of nitrogen dioxide, ozone, particulate matter with an aerodynamic diameter of less

296 Estimates of fine particulate matter (particulate matter with an aerodynamic diameter of up to

297 ed with concentrations of black carbon, fine particulate matter with an aerodynamic with diameter les

298 an association between prenatal exposure to particulate matter with diameter </=10mum (PM10) during

299 er LWP in turn enhance the concentrations of particulate matter with diameter less than 2.5 mum (PM2.

300 rticles are a major component of atmospheric particulate matter, yet their formation processes and am