Abstract

Continuous and simultaneous observational particulate matter (measured as PM10), nitrogen dioxide (NO2) and oxides of nitrogen (NOx) data were captured at a kerbside site alongside a major highway in Auckland, New Zealand, and at a pair of setback sites within 250 m of the highway, day and night over 8 weeks. The three measurement sites were intended to allow emissions from the highway to be largely isolated from other sources. By filtering the data and subtracting upwind concentrations, the average roadside increment was calculated to be 1.8, 7.2 and 101.4 μg m−3 for PM10, NO2 and NOx, respectively, relative to a predominantly upwind setback site, and −0.1, 9.4 and 98.5 μg m−3 for PM10, NO2 and NOx, respectively, relative to a downwind setback site. The negative value for PM10 was attributed to local evening heating sources impacting the setback site. On days when peak 24 h PM10 concentrations were observed, the absolute kerbside increment was 2.1 μg m−3. The absolute roadside 24 h average PM10 increment varied diurnally, peaking (on average) at 2.4 μg m−3 during peak traffic hours. The largest observed 24-h average PM10 roadside increment was 6.9 μg m−3 and exceeded 5 μg m−3 on nine occasions. On each of these occasions, the daily mean wind speed was less than 2 m s−1. The diurnally averaged difference in NOx concentrations between the kerbside site and the setback sites clearly resembled the diurnal cycle in traffic volume, and peaked during the morning traffic peak at around 180 μg m−3. Background NOx concentrations were slightly higher in our study compared to a similar study in Las Vegas but absolute roadside concentrations were higher. This may be consistent with higher NOx emission factors in Auckland, but differences in the precise distance of the monitor from the road lanes and differences in meteorology need to be considered.

Highlights

  • Long-term spatial gradients in air pollutants concentrations exist within cities at the ~100-m scale, and those intra-city gradients are often as significant, if not more so, than inter-city gradients

  • The WHO Guideline of 40 μg m−3 of nitrogen dioxide (NO2) as an annual mean is widely used to judge the health significance of traffic-related air pollution because it is accepted that road traffic emissions are the major source of NO2 concentrations in many urban areas

  • We make the assumption that there is no source or sink between the upwind and downwind sites other than the road source. The result of this design is that the contribution of the road to local air quality can be estimated from the difference in concentrations between downwind and upwind sites

Read more

Summary

Introduction

Long-term spatial gradients in air pollutants concentrations exist within cities at the ~100-m scale, and those intra-city gradients are often as significant, if not more so, than inter-city gradients. The distance between residence and major roads has a significant association with a wide range of adverse health outcomes (HEI 2010). Including these localised gradients increases the estimated burden compared to conventional airshed-scale analyses In lieu of health-based guidance relating to roadside locations, regulatory agencies often use standards and guidelines to represent health-endangering concentrations of air pollution. The WHO Guideline of 40 μg m−3 of nitrogen dioxide (NO2) as an annual mean is widely used to judge the health significance of traffic-related air pollution because it is accepted that road traffic emissions are the major source of NO2 concentrations in many urban areas

Methods
Results
Discussion
Conclusion
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call