Near Road Study Report 2019
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Near-Road Air Pollution Pilot Study Final Report Southern Ontario Centre for Atmospheric Aerosol Research University of Toronto 2019 Executive Summary Context Vehicles emit a complex mixture of air pollutants that can reach wide areas around busy roads. Near-road monitoring of air pollution is needed in order to assess the extent and potential health impacts of the resulting exposure. One-third of Canadians live near major roads and are thus potentially exposed to traffic emissions. This report documents a pilot study conducted between 2015 and 2017 involving six monitoring stations in the cities of Vancouver, British Columbia and Toronto, Ontario. These stations were established beside major roads in order to directly measure traffic-related air pollution and well away from busy roads as comparator urban background sites. Findings Local traffic dominates pollutant concentrations beside major roads Air pollutants associated with vehicles, diesel vehicles in particular, were higher beside roads. For example, over 80% of nitrogen monoxide and 60% of black carbon was found to be coming from local traffic at the near-road sites. Local traffic also contributed up to half of the PM2.5 near roads, with the fraction varying over time. For example, during weekday morning rush hour, almost half of the overall PM2.5 beside Highway 401 in Toronto was due to traffic. Near-road concentrations can vary widely Concentrations of traffic-related air pollutants were typically highest during weekday morning rush hour and decreased in the afternoon and on weekends. Concentrations also decreased by up to a factor of four with increasing wind speed from 1 to 10 m/s and were six times higher when the monitoring station was directly downwind of the road. In general, dilution of vehicle exhaust depended on proximity to the road (i.e., traffic in the closest lanes typically dominated roadside concentrations). However, under stagnant wind conditions, little to no dilution occurred and concentrations were similar across a wide region spanning from the roadside to 150 m away. Near-Road Pollution Study 2019 1 Large trucks contribute disproportionally to emissions Heavy truck traffic produced pollutant concentrations beside a major road that were similar to those beside the busiest stretch of highway in North America, despite being lower in car traffic by a factor of ten. Emission factors were calculated based on measurements over approximately 400 days, consolidating the emissions from 200 million vehicles. These emission factors allowed direct comparisons across the three near-road sites in terms of the amount of pollutant emitted per kilogram of fuel used by vehicles. It was found that variability at and across the three sites depended more on the proportion of large trucks in the fleet than the total traffic volume. Emission factors for over 100,000 individual vehicle plumes also showed that a small portion of the trucks and cars were responsible for the majority of emissions. Policies and programs implemented to remove this small fraction of highest emitting vehicles from populated areas could yield large benefits. Black carbon indicates elevated exposure to diesel exhaust Black carbon can be used as a proxy to estimate exposure to the complex mixture of chemicals in diesel exhaust. The study found roadside levels of black carbon ≈ 1 μg/m3. These levels are in the range that has been associated with an elevated lifetime risk of lung cancer and are 400 times higher than the one in 100,000 risk-factor often used to establish exposure standards for the public. Another common pollutant associated with diesel emissions, nitrogen dioxide, exceeded Canada’s 2020 annual ambient air quality standard of 17 ppb (based on an annual average of hourly measurements) both near the major roads and as far away as 150 m. Canada’s seasons can increase emissions Colder winter temperatures increased near-road concentrations of nitrogen oxides and ultrafine particles. This finding suggests that the emission treatment systems on diesel vehicles may not function effectively under cold winter temperatures. In the case of ultrafine particles, the increase was due to less particle evaporation under colder temperatures. Black carbon was found to be higher in Toronto in summer than winter, suggesting seasonal changes in Ontario diesel fuel formulation may be affecting tailpipe emissions. Notably, this potential influence of fuel composition may offer an effective intervention for reducing black carbon emissions from vehicles. Near-Road Pollution Study 2019 2 As tailpipe emissions drop, non-tailpipe emissions are emerging Improvements to vehicle technologies have led to an overall reduction in the tailpipe emissions of many pollutants. However, this study has revealed that non-tailpipe emissions (brake wear, tire wear and resuspension of road dust) are rising. For example, non-tailpipe emissions are now contributing more PM2.5 than primary tailpipe emissions in downtown Toronto. Moreover, non- tailpipe emissions are changing the composition of PM2.5 by increasing the concentrations of metals such as Ba, Cu, Fe, and Ca beside roads. Near-road sites reflect pollutant concentrations across the city Pollutant levels measured through sampling across Toronto with a mobile lab (on highways, arterial roads, and quiet streets) were similar to those measured at the near-road monitoring sites. Thus, the pollutant concentrations at the near-road sites appear to be representative of other near-road locations across the city with equivalent vehicle fleet characteristics. Thus near-road monitoring can capture the wide range in exposure to traffic pollutants that is being experienced by residents across a city. Recommendations Creating a national network A national near-road monitoring network is needed and should include long-term near-road monitoring stations established in Canada’s largest cities. A national near-road monitoring network should support development of policies or guidelines (e.g. siting facilities for vulnerable populations) and assessing the effectiveness of potential air quality or climate-related interventions. Relevant stakeholders should be engaged from the outset in order to consider in advance how the data will be used and by whom. A national network for near-road monitoring should promote outreach and public involvement, to proactively engage Canadians, encourage behaviour change and build stronger societal support for new policies or regulations. Near-Road Pollution Study 2019 3 A national network for near-road monitoring should publicly share data from near-road stations through web sites, phone apps, and public displays (e.g., electronic signs on highways) when and where impacts are potentially arising. A national network for near-road monitoring should have a three-tiered design with: i) permanent stations, ii) easily deployable enclosures with selected instruments for shorter-term monitoring, and iii) widespread networks of inexpensive sensor technologies implemented as part of smart city initiatives. The scale of a national network for near-road monitoring should strategically balance the coverage achieved with the resources required. This process should be informed by considering the risks related to only monitoring at selected locations and the potential severity of impacts that might thereby go undetected. A national network for near-road monitoring should establish metrics to assess the effectiveness and adequacy of the program. These metrics should guide decisions on creating, relocating, or terminating monitoring stations or instruments. Suggested metrics include data completeness and reliability of instruments; the degree of variability in observations over time or across sites; and the focus and level of use of resulting data by researchers, policy developers, and the public. Station design and placement Site selection for stations should provide geographic coverage across Canada and take into consideration population and traffic density. The near-road stations should be designed to be flexible and adaptable. Capacity and space within stations should be adequate so that instruments can be rotated across stations and evolve as new vehicle technologies and pollutants emerge. Urban background stations are not essential to enabling near-road monitoring. Therefore, it is recommended that additional background stations not be included as a core component of the near-road monitoring network. However, urban background stations can provide useful data for a range of other research applications and it is thus recommended that the continuing operation of existing background stations be considered on a case-by-case basis. Near-Road Pollution Study 2019 4 Measurement methods Near-road stations should all be equipped with high-quality instruments to measure NOx, CO, CO2, PM2.5, UFP, BC, traffic volume, vehicle types, and meteorological data in order to create a backbone for traffic-related air pollution monitoring across the country. Additional pollutants such as SO2 and O3 may also be included depending on the pre-existing availability of other nearby measurements. PM2.5 speciation and organic gases should be measured some of the time or at some of the stations. This partial coverage might be achieved by rotating higher time-resolution instruments annually across stations or, if using twenty-four-hour integrated sample collection, rotating samplers or only making measurements every six days. Policy implications Policies should be implemented to identify and remove