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[School] Buses/Vehicle Use around schools | Air Pollution and Academic Achievement | Air Pollution and Children's Health | Air Pollution and COVID-19 | Air Pollution/Climate Change and Health | Air Pollution/Climate Change and Mental Health | Indoor Air Pollution | Systemic Environmental Racism | Vehicles/Traffic
Read bios and background on this film covering the history of Old Smokey, the former incinerator, which operated from 1925 to 1970, and its environmental health impact on the West Grove community.
Published Nov 14, 2017
Law, U. of M. S. of. (2017). āOld Smokey: A Community History.ā University of Miami School of Law. https://issuu.com/miamilaw/docs/ceps_oral_20history_20film_20projec
Electrification has been rapidly promoted to transform the energy source for public transit buses. Among all electric technologies penetrating the public bus fleet, battery electric buses (BEBs) dominates the market. Nevertheless, real-world energy consumption (EC) is of great concern, since BEBs are often used under congested conditions that may affect their energy and environmental benefits. This study proposes an operating mode binning method to assess on-road EC and well-to-wheel (WTW) air pollutants emissions of BEBs under complex real-world usage patterns. Second-by-second EC and operating data of two BEBs demonstrated in Macao, China is adopted to establish the EC profiles under each micro modes. Results show that EC value would be below zero in certain operation modes with negative vehicle specific power values, which suggests the regenerative brake system is effectively functioning under deceleration conditions. Average EC are estimated to be 1.7 to 4.1 kWh kmā1 for BEB12 and 1.2 to 2.9 kWh kmā1 for BEB10 (i.e., vehicle length of 12 m and 10 m), respectively, under all operating conditions (i.e., 18 various patterns) by average speed, loading mass and air conditioner usage. The large variation in real-world EC would proportionally affect WTW emissions of carbon dioxide (CO2) and air pollutants from BEBs. When deployed in Macao where non-fossil electricity is relatively abundant, BEB can significantly reduce WTW emissions of nitrogen oxides (NOX) and volatile organic compounds (VOC) by 60%ā80%, along with considerable reductions of 10%ā40% for CO2 and fine particulate matters (PM2.5). Further, the benefits related to WTW CO2 and PM2.5 emissions would not exist if BEBs are deployed in coal power-rich regions. Our measurement results and WTW emission suggests that current fuel economy testing procedure of BEB should be modified to better inform customers and policy-makers of their real-world performance and benefits.
Published Oct 17, 2017
He, X., Zhang, S., Ke, W., Zheng, Y., Zhou, B., Liang, X., & Wu, Y. (2018). Energy consumption and well-to-wheels air pollutant emissions of battery electric buses under complex operating conditions and implications on fleet electrification. Journal of Cleaner Production, 171, 714ā722. https://doi.org/10.1016/j.jclepro.2017.10.017
A child's exposure to environmental pollutants can have life-long health effects. Thus it is critical to understand the potential exposure pathways. In this paper, we examine the increase in ambient PM2.5 concentrations at schools from private vehicle use for dropping children off at school. In North America, students are commonly driven to school in a private vehicle. Additionally, students walk or cycle, or take a school bus. Our vehicle surveys recorded between 23 and 116 personal vehicles at 25 schools, where enrolment ranged from 160 to 765 students. We fit a linear regression model to predict the number of vehicles at schools we did not observe within our study area, which explained 57% of the variation in our surveys. A microsimulation traffic model was created for each of the 86 schools we studied. Outputs from the traffic model were used to determine the emissions generated at each school. PM2.5 emissions varied from 0.14 to 6.38 g. Lastly, we dispersed the emissions produced by private vehicles dropping off students, which are emissions generated by unnecessary trips because students further than walking distance are provided transportation by the school board. At the drop-off location in front of the school, we found ambient concentration increases of at least 5 μg/m3, 10 μg/m3, 25 μg/m3 and 50 μg/m3 during 16.8%, 7.6%, 2.0% and 0.5% of the mornings, respectively. This research was conducted in a medium-sized North American city and should allow transferability to similar cities. We conclude that the use of private vehicles can significantly increase local concentrations, regardless of background conditions.
Published Sep 1, 2017
Adams, M. D., & Requia, W. J. (2017). How private vehicle use increases ambient air pollution concentrations at schools during the morning drop-off of children. Atmospheric Environment, 165, 264ā273. https://doi.org/10.1016/j.atmosenv.2017.06.046
Although numerous studies have demonstrated links between particulate matter (PM) and adverse health effects, the chemical components of the PM mixture that cause injury are unknown. Objectives: This work characterizes spatial and temporal variability of PM2.5 (PM with aerodynamic diameter < 2.5 μm) components in the United States; our objective is to identify components for assessment in epidemiologic studies. Methods: We constructed a database of 52 PM2.5 component concentrations for 187 U.S. counties for 2000-2005. First, we describe the challenges inherent to analysis of a national PM2.5 chemical composition database. Second, we identify components that contribute substantially to and/or co-vary with PM2.5 total mass. Third, we characterize the seasonal and regional variability of targeted components. Results: Strong seasonal and geographic variations in PM2.5 chemical composition are identified. Only seven of the 52 components contributed ℠1% to total mass for yearly or seasonal averages [ammonium (NH4+), elemental carbon (EC), organic carbon matter (OCM), nitrate (NO3-), silicon, sodium (Na+), and sulfate (SO42-)]. Strongest correlations with PM2.5 total mass were with NH4+ (yearly), OCM (especially winter), NO3- (winter), and SO42- (yearly, spring, autumn, and summer), with particularly strong correlations for NH4+ and SO42- in summer. Components that co-varied with PM2.5 total mass, based on daily detrended data, were NH4+, SO42-, OCM, NO3-, bromine, and EC. Conclusions: The subset of identified PM2.5 components should be investigated further to determine whether their daily variation is associated with daily variation of health indicators, and whether their seasonal and regional patterns can explain the seasonal and regional heterogeneity in PM10 (PM with aerodynamic diameter < 10 μm) and PM2.5 health risks.
Published Jul 1, 2017
Bell, M. L., Dominici, F., Ebisu, K., Zeger, S. L., & Samet, J. M. (2007). Spatial and temporal variation in PM2.5 chemical composition in the United States for health effects studies. In Environmental Health Perspectives (Vol. 115, Issue 7, pp. 989ā995). https://doi.org/10.1289/ehp.9621
Reports the results of a large study, including more than 60 million Medicare beneficiaries from the years 2000 through 2012, that addresses the association between annual average levels of PM2.5 and ozone,9 as measured at the ZIP Code level, and mortality. For every increase of 10 μg per cubic meter in PM2.5, there was an associated 7.3% increase in all-cause mortality (95% confidence interval [CI], 7.1 to 7.5), after adjustment for demographic characteristics, Medicaid eligibility, and area-level covariates. Below the current NAAQS for PM2.5 of 12 μg per cubic meter, the data showed that each increase in PM2.5 of 10 μg per cubic meter was associated with an even greater increase (13.6%) in mortality (95% CI, 13.1 to 14.1). There was no appreciable level below which the risk of death tapered off ā and thus no āsafeā level of PM2.5. Owing to the large size of the cohort, Di et al. were able to perform robust subgroup analyses and identified greater risks of death associated with air pollutants among blacks and Medicaid-eligible populations; moreover, these groups were more likely to be exposed to higher pollutant levels.
Published Jun 29, 2017
Berger, R. E., Ramaswami, R., Solomon, C. G., & Drazen, J. M. (2017). Air pollution still kills. New England Journal of Medicine, 376(26), 2591ā2592. https://doi.org/10.1056/NEJMe1706865
Studies have shown that long-term exposure to air pollution increases mortality. However, evidence is limited for air-pollution levels below the most recent National Ambient Air Quality Standards. Previous studies involved predominantly urban populations and did not have the statistical power to estimate the health effects in underrepresented groups. METHODS We constructed an open cohort of all Medicare beneficiaries (60,925,443 persons) in the continental United States from the years 2000 through 2012, with 460,310,521 person-years of follow-up. Annual averages of fine particulate matter (particles with a mass median aerodynamic diameter of less than 2.5 μm [PM2.5]) and ozone were estimated according to the ZIP Code of residence for each enrollee with the use of previously validated prediction models. We estimated the risk of death associated with exposure to increases of 10 μg per cubic meter for PM2.5 and 10 parts per billion (ppb) for ozone using a two-pollutant Cox proportionalhazards model that controlled for demographic characteristics, Medicaid eligibility, and area-level covariates. RESULTS Increases of 10 μg per cubic meter in PM2.5 and of 10 ppb in ozone were associated with increases in all-cause mortality of 7.3% (95% confidence interval [CI], 7.1 to 7.5) and 1.1% (95% CI, 1.0 to 1.2), respectively. When the analysis was restricted to person-years with exposure to PM2.5 of less than 12 μg per cubic meter and ozone of less than 50 ppb, the same increases in PM2.5 and ozone were associated with increases in the risk of death of 13.6% (95% CI, 13.1 to 14.1) and 1.0% (95% CI, 0.9 to 1.1), respectively. For PM2.5, the risk of death among men, blacks, and people with Medicaid eligibility was higher than that in the rest of the population. CONCLUSIONS In the entire Medicare population, there was significant evidence of adverse effects related to exposure to PM2.5 and ozone at concentrations below current national standards. This effect was most pronounced among self-identified racial minorities and people with low income. (Supported by the Health Effects Institute and others.)
Published Jun 29, 2017
Di, Q., Wang, Y., Zanobetti, A., Wang, Y., Koutrakis, P., Choirat, C., Dominici, F., & Schwartz, J. D. (2017). Air pollution and mortality in the medicare population. New England Journal of Medicine, 376(26), 2513ā2522. https://doi.org/10.1056/NEJMoa1702747
BACKGROUND: Daily changes in ambient concentrations of particulate matter, nitrogen oxides and ozone are associated with increased cardiopulmonary morbidity and mortality, with the lungs and their function being a vulnerable target. METHODS: To evaluate the association between daily changes in air pollution and lung function in healthy adults we obtained annual lung function measurements from a routine worker health surveillance program not designed for research purposes. Forced Vital Capacity (FVC), Forced Expiratory Volume in the first second (FEV1), FEV1/FVC and Peak Expiratory flow (PEF) from a cohort of 2449 employees were associated with daily measurements of PM10, NO2 and ozone at a nearby monitoring station in the North of Belgium. Repeated measures were available for the period 2011-2015. RESULTS: The mean (SD) PM10 concentration on the day of the lung function test was 24.9 (15.5) μg/m3. A 10 μg PM10/m3 increase on the day of the clinical examination was associated with a 18.9 ml lower FVC (95% CI: -27.5 to -10.3, p < 0.0001), 12.8 ml lower FEV1 (-19.1 to -6.5; p < 0.0001), and a 51.4 ml/s lower PEF (-75.0 to -27.0; p < 0.0001). The FEV1/FVC-ratio showed no associations. An increase of 10 μgNO2/m3 was associated with a reduction in PEF (-66.1 ml/s (-106.6 to -25.6; p < 0.001)) on the day of the examination. CONCLUSIONS: We found negative associations between daily variations in ambient air pollution and FVC, FEV1 and PEF in healthy adults.
Published Jun 14, 2017
Int Panis, L., Provost, E. B., Cox, B., Louwies, T., Laeremans, M., Standaert, A., Dons, E., Holmstock, L., Nawrot, T., & De Boever, P. (2017). Short-term air pollution exposure decreases lung function: a repeated measures study in healthy adults. Environmental Health : A Global Access Science Source, 16(1), 60. https://doi.org/10.1186/s12940-017-0271-z
How school location impacts childrenās air pollution exposure and their ability to walk and bike to school has been a growing policy issue. Smart growth advocates encourage districts to locate schools in āwalkableā locations, often near high-volume roadways while health professionals emphasize the importance of minimizing exposure to high levels of air pollution and distance schools from major roads. As states consider or implement laws to site schools away from high-volume roadways, such policies can lead to school locations disconnected from neighborhoods and accessible only by motorized transport modes. This study analyzes childrenās air pollution exposure across an average school day, analyzing variation across roadway characteristics, local school and home environment, and mode choice for school commute. This research compares daily average exposures for children walking to a local school in a high-traffic area versus exposures if they were required to be bussed or driven to a distant, āgreenerā school located in a low-traffic environment. Daily average exposures to air pollution were estimated across an average school day (AM Commute, Unload, School Day, Load, PM Commute). The analysis also assesses how pollution exposure can be mitigated through clean school bus technology, improved HVAC systems, and no-idling policies. Bussing children from a high-traffic neighborhood to a distant school in a low-traffic environment resulted in average daily exposures from 2 to 4 times higher than children walking to their local school. The authors' simulated school siting policy assessment found that bussing children to a distant school in a ācleanerā air quality school site did not reduce average daily personal exposure of children who would otherwise walk or be driven/bussed to their local school in a ādirtierā air quality site. Mitigation measures like a clean bus fleet greatly reduce exposures for children bussing longer distances to a distant school while school HVAC improvements in a heavy-diesel/heavy-traffic school environment yield more conservative reductions.
Published Jun 1, 2017
Wolfe, M., McDonald, N., Arunachalam, S., & Valencia, A. (2017). Air Pollution Exposure during School Commutes. Journal of Transport & Health, 5, S48āS49. https://doi.org/10.1016/j.jth.2017.05.339
Although exposure to traffic emissions is frequently associated with negative health impacts, few studies have measured air pollution directly in-vehicle, and limited measurements of daily commuter exposure exist. This research, part of the Atlanta Commuter Exposures (ACE) Study, assesses on-roadway in-cabin particulate pollution (PM 2.5 ) collected from scripted rush hour commutes on highways and on non-highway side streets. Water-soluble extracts from PM 2.5 filters were analyzed for oxidative potential of water-soluble species using the dithiothreitol (DTT) assay, and results suggest that there may be substantial gas-phase DTT activity in fresh emissions. We measured DTTv activities (i.e., DTT activity normalized to the sampled air volume) that were on average two times higher than comparable measurements collected by stationary roadside monitoring sites. Although some of this difference may be attributable to positive artifacts due to relatively brief (2-h) quartz filter sampling durations, the current findings provide some indication that commuters encounter notably higher exposure to redox-active PM 2.5 in the on-road environment. Strong correlations are observed between water-soluble DTT activity and water-soluble organic carbon (WSOC), specifically for the āsemivolatileā WSOC component (measured as the difference between denuded and non-denuded filters). Although potential for artifacts when measuring DTT activity of fresh emissions using filter-based methods is considerable, these results suggest that semivolatile organic species are important contributors to DTT activity, at least in environments where ambient PM 2.5 is dominated by vehicular sources.
Published Jun 1, 2017
Vreeland, H., Weber, R., Bergin, M., Greenwald, R., Golan, R., Russell, A. G., Verma, V., & Sarnat, J. A. (2017). Oxidative potential of PM 2.5 during Atlanta rush hour: Measurements of in-vehicle dithiothreitol (DTT) activity. Atmospheric Environment, 165, 169ā178. https://doi.org/10.1016/j.atmosenv.2017.06.044
Lung function in early life has been shown to be an important predictor for peak lung function in adults and later decline. Reduced lung function per se is associated with increased morbidity and mortality. With this review, we aim to summarize the current epidemiological evidence on the effect of traffic-related air pollution on lung function in children and adolescents. We focus in particular on time windows of exposure, small airway involvement, and vulnerable sub-groups in the population. Findings from studies published to date support the notion that exposure over the entire childhood age range seems to be of importance for lung function development. We could not find any conclusive data to support evidence of sup-group effects considering gender, sensitization status, and asthma status, although a possibly stronger effect may be present for children with asthma. The long-term effects into adulthood of exposure to air pollution during childhood remains unknown, but current studies suggest that these deficits may be propagated into later life. In addition, further research on the effect of exposure on small airway function is warranted.
Published May 27, 2017
Schultz, E.S., Litonjua, A.A. & MelƩn, E. Effects of Long-Term Exposure to Traffic-Related Air Pollution on Lung Function in Children. Curr Allergy Asthma Rep 17, 41 (2017). https://doi.org/10.1007/s11882-017-0709-y