Quantification of vehicle fleet PM10 particulate matter emission factors from exhaust and non-exhaust sources using tunnel measurement techniques
- 1. Centre for Atmospheric and Instrumentation Research (CAIR), University of Hertfordshire, Hatfield, Hertfordshire AL10 9AB (United Kingdom)
- 2. School of Public Health, Post Graduate Institute of Medical Education and Research (PGIMER), Chandigarh 160012 (India)
Description
Road tunnels act like large laboratories; they provide an excellent environment to quantify atmospheric particles emission factors from exhaust and non-exhaust sources due to their known boundary conditions. Current work compares the High Volume, Dichotomous Stacked Filter Unit and Partisol Air Sampler for coarse, PM10 and PM2.5 particle concentration measurement and found that they do not differ significantly (p = 95%). PM2.5 fraction contributes 66% of PM10 proportions and significantly influenced by traffic (turbulence) and meteorological conditions. Mass emission factors for PM10 varies from 21.3 ± 1.9 to 28.8 ± 3.4 mg/vkm and composed of Motorcycle (0.0003–0.001 mg/vkm), Cars (26.1–33.4 mg/vkm), LDVs (2.4–3.0 mg/vkm), HDVs (2.2–2.8 mg/vkm) and Buses (0.1 mg/vkm). Based on Lawrence et al. (2013), source apportionment modelling, the PM10 emission of brake wear (3.8–4.4 mg/vkm), petrol exhaust (3.9–4.5 mg/vkm), diesel exhaust (7.2–8.3 mg/vkm), re-suspension (9–10.4 mg/vkm), road surface wear (3.9–4.5 mg/vkm), and unexplained (7.2 mg/vkm) were also calculated. The current study determined that the combined non-exhaust fleet PM10 emission factor (16.7–19.3 mg/vkm) are higher than the combined exhaust emission factor (11.1–12.8 mg/vkm). Thus, highlight the significance of non-exhaust emissions and the need for legislation and abatement strategies to reduce their contributions to ambient PM concentrations. - Highlights: • Calculations of exhaust/non-exhaust particulate emission factors using tunnel sampling and source apportionment techniques. • Non-exhaust emission dominates in the fine particle fraction, considered responsible for adverse human health impacts. • Emission factors for non-exhaust sources (e.g. tyre and brake) were calculated. • Fleet source PM10 emission factor were also calculated, which can be used in dispersion modelling and health risk assessment. • Tukey mean-difference plot shows good fit of measured emission factors with NAEI 2008 emission factors. - Combined non-exhaust fleet PM10 emission factor (16.7–19.3 mg/vkm) are higher than the combined exhaust emission factor (11.1–12.8 mg/vkm).
Availability note (English)
Available from http://dx.doi.org/10.1016/j.envpol.2016.01.011Additional details
Identifiers
- DOI
- 10.1016/j.envpol.2016.01.011;
- PII
- S0269-7491(16)30011-2;
Publishing Information
- Journal Title
- Environmental Pollution (1987)
- Journal Volume
- 210
- Journal Page Range
- p. 419-428
- ISSN
- 0269-7491
- CODEN
- ENPOEK
INIS
- Country of Publication
- United Kingdom
- Country of Input or Organization
- International Atomic Energy Agency (IAEA)
- INIS RN
- 48046163
- Subject category
- S54: ENVIRONMENTAL SCIENCES;
- Descriptors DEI
- AIR POLLUTION; AUTOMOBILES; BUSES; COARSE PARTICLES; ECOLOGICAL CONCENTRATION; FINE PARTICLES; HEALTH HAZARDS; MOTORCYCLES; PUBLIC HEALTH; RISK ASSESSMENT; TUNNELS
- Descriptors DEC
- HAZARDS; PARTICLES; POLLUTION; UNDERGROUND FACILITIES; VEHICLES
Optional Information
- Copyright
- Copyright (c) 2016 Elsevier Science B.V., Amsterdam, The Netherlands, All rights reserved.