2020
DOI: 10.1016/j.trd.2020.102442
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Influence of roadway emissions on near-road PM2.5: Monitoring data analysis and implications

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Cited by 33 publications
(29 citation statements)
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“…No distinction is made between daily average FRM and FEM (with ≥18 h of hourly measurements) values for the daily interpolation because they are both high-confidence, quality-assured measurements that are used for regulatory purposes such as calculating design interpolation have the same model of FEM deployed at both the near-road and non-near-road sites, reducing any methodspecific variation in the PM 2.5 measurement related to chemical composition. 20 Although not officially part of the Near-Road Network, several existing sites with NO 2 or PM 2.5 monitors are very close to major highways or roadway features. These quasi-near-road sites may have a longer record of NO 2 or PM 2.5 measurements than the newer, officially designated near-road sites and can be used to show long-term trends in the near-road increment.…”
Section: ■ Introductionsupporting
confidence: 90%
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“…No distinction is made between daily average FRM and FEM (with ≥18 h of hourly measurements) values for the daily interpolation because they are both high-confidence, quality-assured measurements that are used for regulatory purposes such as calculating design interpolation have the same model of FEM deployed at both the near-road and non-near-road sites, reducing any methodspecific variation in the PM 2.5 measurement related to chemical composition. 20 Although not officially part of the Near-Road Network, several existing sites with NO 2 or PM 2.5 monitors are very close to major highways or roadway features. These quasi-near-road sites may have a longer record of NO 2 or PM 2.5 measurements than the newer, officially designated near-road sites and can be used to show long-term trends in the near-road increment.…”
Section: ■ Introductionsupporting
confidence: 90%
“…For the hourly PM 2.5 interpolation, only CBSAs with FEM monitors at near-road and non-near-road sites are considered. Most CBSAs that qualify for the hourly PM 2.5 interpolation have the same model of FEM deployed at both the near-road and non-near-road sites, reducing any method-specific variation in the PM 2.5 measurement related to chemical composition …”
Section: Data and Methodsmentioning
confidence: 99%
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“…Here, we only evaluate the GEOS-Chem simulations with U.S. Embassy and Consulates’ monitors for reasons discussed elsewhere 13 and the strict quality assurance/quality control procedures used in the Embassy monitoring. 60 Negative concentrations were removed from the observational data set, and we only consider daily data where 75% of hours were recorded, broadly consistent with procedures outlined by Mukherjee et al 61 Normalized mean bias was calculated between the simulated results and the average of the observations and satellite products. We report population-weighted concentrations and use the same population distribution data as outlined in previous work utilizing this inventory.…”
Section: Methodsmentioning
confidence: 99%
“…The adverse effects of long term exposure to PM 2.5 (10 μg/m 3 annual mean), PM 10 (20 μg/m 3 annual mean) (particulates with aerodynamic diameter <2.5μm and <10μm, respectively) on human health in terms of cardio-respiratory adversities, cancer and neurological effects have been widely covered in epidemiological studies [ 6 12 ]. Elevated localized PM 2.5 levels are specifically reported to be much higher near the highway owing to vehicular emissions compared to the far-field regions [ 13 16 ]. These fine emission particles get deposited in the lower respiratory tract and trigger local and systemic inflammation [ 17 ] which in turn may set off a cascade of metabolic reactions.…”
Section: Introductionmentioning
confidence: 99%