2009
DOI: 10.1289/ehp.0800185
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Emergency Admissions for Cardiovascular and Respiratory Diseases and the Chemical Composition of Fine Particle Air Pollution

Abstract: BackgroundPopulation-based studies have estimated health risks of short-term exposure to fine particles using mass of PM2.5 (particulate matter ≤ 2.5 μm in aerodynamic diameter) as the indicator. Evidence regarding the toxicity of the chemical components of the PM2.5 mixture is limited.ObjectiveIn this study we investigated the association between hospital admission for cardiovascular disease (CVD) and respiratory disease and the chemical components of PM2.5 in the United States.MethodsWe used a national datab… Show more

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Cited by 493 publications
(323 citation statements)
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“…*Published emission factors but not reported in text. **Emission factors reported explicitly in text ᴬ Age groups according to health outcomes; ᴯ Such as ≥18 years or ≥30 years; C Environmental Benefits Mapping and Analysis Program using the concentration response function from chronic bronchitis [63], acute bronchitis [64], all-cause mortality [65,104], COPD hospitalization (Moolgavgkar 2000a, 2003) [66], asthma emergency room visits [67], work loss days [68], asthma (symptoms) [69], minor-restricted activity days [70], acute MI [71], respiratory disease [72], lower respiratory symptoms [73], and cough among asthmatic children [74]; D Probable, but not specified explicitly in the text; ᴱ Health And Air Pollution Study in New Zealand to estimate the morbidity and mortality health costs associated with traffic emissions [82]; F CVD admission >64 years: [75]; ᴳ Mortality: <75 and >75 years, respiratory disease (65 years) [76], and lung cancer [104] Morbidity: CVD, respiratory disease [76], and lung cancer [104]; H Method of transport emission estimation is quite vague in determination of emission factors; I External cost of energy to estimate the automotive pollution impact on health in Europe [81]; J Cerebrovascular disease and lower respiratory tract infection [77], preterm weight [78], low term weight [79], and CVD (Mustafic 2012) [80]; K Value of a Life Year: calculation of monetary benefits of mortality reduction using a life tables approach. …”
Section: Resultsmentioning
confidence: 99%
“…*Published emission factors but not reported in text. **Emission factors reported explicitly in text ᴬ Age groups according to health outcomes; ᴯ Such as ≥18 years or ≥30 years; C Environmental Benefits Mapping and Analysis Program using the concentration response function from chronic bronchitis [63], acute bronchitis [64], all-cause mortality [65,104], COPD hospitalization (Moolgavgkar 2000a, 2003) [66], asthma emergency room visits [67], work loss days [68], asthma (symptoms) [69], minor-restricted activity days [70], acute MI [71], respiratory disease [72], lower respiratory symptoms [73], and cough among asthmatic children [74]; D Probable, but not specified explicitly in the text; ᴱ Health And Air Pollution Study in New Zealand to estimate the morbidity and mortality health costs associated with traffic emissions [82]; F CVD admission >64 years: [75]; ᴳ Mortality: <75 and >75 years, respiratory disease (65 years) [76], and lung cancer [104] Morbidity: CVD, respiratory disease [76], and lung cancer [104]; H Method of transport emission estimation is quite vague in determination of emission factors; I External cost of energy to estimate the automotive pollution impact on health in Europe [81]; J Cerebrovascular disease and lower respiratory tract infection [77], preterm weight [78], low term weight [79], and CVD (Mustafic 2012) [80]; K Value of a Life Year: calculation of monetary benefits of mortality reduction using a life tables approach. …”
Section: Resultsmentioning
confidence: 99%
“…The 1-min PM and BC concentrations were matched to the speed of the vehicle during that minute, as recorded by the GPS device. When the relationships between PM 1 , PM [1][2][3][4][5][6][7][8][9][10] and BC concentrations and average vehicle speed were examined, no clear differences were observed. Furthermore, when PM and BC concentrations were related to the type of road, road type did not have an effect on in-vehicle PM and BC concentrations.…”
Section: Resultsmentioning
confidence: 99%
“…In-vehicle PM 1 concentration was significantly associated with ambient PM 2.5 mass concentration (linear regression analysis, r 2 ϭ 0.65, P Ͻ 0.0001). However, in-vehicle PM [1][2][3][4][5][6][7][8][9][10] (linear regression analysis, r 2 ϭ 0.46, P Ͻ 0.0001) and BC (linear regression analysis, r 2 ϭ 0.14 P ϭ 0.022) concentrations were moderately associated with ambient PM 2.5 mass concentrations.…”
Section: Resultsmentioning
confidence: 99%
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“…1 Nationwide and multiple-community studies report that exposure to PM 2.5 is linked with an increased risk of hospital admissions and mortality in the US, and that certain PM 2.5 species may be more toxic than others. [2][3][4][5] DNA methylation is an epigenetic process in which a methyl group is added to deoxycytosine bases to form deoxymethylcytosine. The literature to date indicates that DNA methylation may be an important pathway linking particulate matter (PM) to health outcomes.…”
Section: Introductionmentioning
confidence: 99%