Abstract

It is well documented that a large portion of urban particulate matters is derived from road dust. Isolating particles of RD which are small enough to be inhaled, however, is a difficult process. In this study, it is shown for the first time that the < 38 µm fraction of road dust particles can be used as a proxy for road dust particles < 10 µm in bioaccessibility studies. This study probed similarities between the < 10 and < 38µm fractions of urban road dust to show that the larger of the two can be used for analysis for which larger sample masses are required, as is the case with in vitro analysis. Road dust, initially segregated to size < 38 µm using sieves, was again size segregated to < 10 µm using water deposition. Both the original < 38 µm and the separated < 10 µm fractions were then subject to single particle analysis by SEM–EDX and bulk analysis by ICP-OES for its elemental composition. Dissolution tests in artificial lysosomal fluid, representative of lung fluid, were carried out on both samples to determine % bioaccessibility of selected potentially harmful elements and thus probe similarities/differences in in vitro behaviour between the two fractions. The separation technique achieved 94.3% of particles < 10 µm in terms of number of particles (the original sample contained 90.4% as determined by SEM–EDX). Acid-soluble metal concentration results indicated differences between the samples. However, when manipulated to negate the input of Si, SEM–EDX data showed general similarities in metal concentrations. Dissolution testing results indicated similar behaviour between the two samples in a simulated biological fluid.

Highlights

  • Urban air quality is of significant importance to the majority of us living or working in our cities worldwide

  • The aim of this study is to see if \ 38 lm fraction of road dust (RD) is analogous to the \ 10 lm fraction, and assess the possibility of using the larger, more abundant size fraction of RD as a proxy for metals in airborne respirable particles originating from RD

  • Presenting particle size distribution data in this manner is common for particulate matter (Chen et al 1997; Lin et al 2005; Potgieter-Vermaak et al 2012; Yue et al 2013) and RD (McKenzie et al 2008); these studies tend to log the number of particles in each bin

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Summary

Introduction

Urban air quality is of significant importance to the majority of us living or working in our cities worldwide. Organization estimates that air pollution is responsible for 8% of lung cancer deaths, 5% of cardiopulmonary deaths and 3% of respiratory infection deaths (WHO 2009). Such deleterious effects on the population are often attributed to particulate matter (PM). (Wang et al 2016) Another large source of PM is believed to be resuspended road dust (RD), which can account for as much as 74% of total suspended particles by mass (Hien et al 1999; Harrison et al 1997) and has been observed to be the largest and second largest contributor to PM10 and PM2.5, respectively (Landis et al 2017). Emphasis on RD as possibly the most significant contributor to PM will continue to grow because of difficulty regulating this substance and its many contributing materials, unlike vehicle exhaust emissions (Padoan et al 2017)

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