Roadside air monitoring in Ontario
Vehicles are a major source of air pollution in Ontario. Traffic-related air pollution is emitted from vehicle exhausts, fuel evaporation, and non-tailpipe sources such as brakes, tires and road dust. Elevated levels of traffic-related air pollution can be found up to 250 meters from a major road.
Exposure to traffic-related air pollutants has been linked to a wide range of adverse health outcomes, including respiratory and cardiovascular diseases, cancer, adverse birth and developmental outcomes, and premature mortality. Children, seniors, and people with pre-existing health conditions are more vulnerable to the adverse health effects from traffic-related pollution.
In 2015, Ontario, in collaboration with Environment and Climate Change Canada, established a dedicated roadside air monitoring network, the first of its kind in Canada, to better understand traffic-related air pollution in highly urbanized settings. These three dedicated roadside air monitoring stations monitor common air pollutants as well as the traffic-related pollutants such as NO2, PM2.5, ultrafine particles, black carbon, metals, and major components of PM2.5. The ministry has also designated 10 of its AQHI air monitoring stations located near major roads as roadside air monitoring stations to complement the dedicated roadside air monitoring network.
Roadside air monitoring stations
This is a map depicting the three dedicated and ten AQHI roadside air monitoring stations across Ontario that were in operation during 2023.
Note:
- Roadside air monitoring stations are located typically within approximately 100 m of a major roadway with daily traffic volumes greater than 10,000 vehicles per day.
Nitrogen dioxide
Combustion or burning of carbon-based materials (e.g., wood, gasoline) in air produces nitrogen oxides (NOx), of which NO2 is a component. The transportation sector is the main source of nitrogen dioxide in Ontario.
Highlights
8-year trends
- NO2 concentrations across the roadside air monitoring network have decreased by 20%.
2023 results
- No exceedances of Ontario’s 1-hour and 24-hour Ambient Air Quality Criteria (AAQC) of 200 ppb and 100 ppb, respectively.
8-year trends
Trend of NO2 annual means across the roadside air monitoring network, 2016-2023
This is a line graph showing the trend of NO2 annual mean concentrations across the roadside air monitoring network from 2016 to 2023. The NO2 annual mean concentrations decreased by 20% over this 8-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 8-year trend is based on data from 12 roadside air monitoring stations.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
The 8-year trend for NO2 at individual roadside air monitoring stations in Ontario is presented in the Appendix: 8-year trend for nitrogen dioxide.
2023 results
Averaging time | Low range | High range | Number of sites with AAQC exceedances |
---|---|---|---|
NO2 1-hour max | 31.4 ppb at North Bay | 91.1 ppb at Toronto Downtown | 0 |
NO2 24-hour max | 17.0 ppb at North Bay | 39.8 ppb at Toronto Downtown | 0 |
NO2 annual mean | 2.9 ppb at North Bay | 14.1 ppb at Toronto Downtown | Not applicable |
A summary of the 2023 NO2 annual statistics for individual roadside air monitoring stations is detailed in the Appendix: 2023 nitrogen dioxide (NO2) annual statistics for the roadside air monitoring network.
Fine particulate matter
Fine particulate matter consists of primary and secondary PM2.5. Primary PM2.5 is emitted directly to the atmosphere. Major sources of primary PM2.5 include residential fireplaces and wood stoves, motor vehicles, smelters, power plants, industrial facilities, and agricultural burning and wildfires. Secondary PM2.5 is formed indirectly in the atmosphere through a series of complex chemical reactions of gaseous precursors such as nitrogen dioxide and sulphur dioxide.
Highlights
8-year trends
- No trend in PM2.5 concentrations across the roadside air monitoring network.
2023 results
- All 13 roadside air monitoring stations measured above the 24-hour reference level of 27 µg/m3 on at least one occasion.
- 9 roadside air monitoring stations measured above the annual reference level of 8.8 µg/m3.
8-year trends
Trend of PM2.5 annual means across the roadside air monitoring network, 2016-2023
This is a line graph showing the trend of PM2.5 annual mean concentrations across the roadside air monitoring network from 2016 to 2023. There was no trend over this 8-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 8-year trend is based on data from 12 roadside air monitoring stations.
- Ontario uses the annual PM2.5 CAAQS “as is” for comparison to a single annual average of air quality data; this value, 8.8 µg/m3, is considered a Reference Level.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
The 8-year trend for PM2.5 at individual roadside air monitoring stations in Ontario is presented in the Appendix: 8-year trend for fine particulate matter.
2023 results
Averaging time | Low range | High range | Number of sites with reference level exceedances |
---|---|---|---|
PM2.5 1-hour max | 98 µg/m3 at Thunder Bay | 668 µg/m3 at North Bay | Not applicable |
PM2.5 24-hour max | 33.8 µg/m3 at Thunder Bay | 400.4 µg/m3 at North Bay | 13 |
PM2.5 annual mean | 6.17 µg/m3 at Thunder Bay | 10.88 µg/m3 at Windsor West | 9 |
The wildfire smoke events in 2023 were unprecedented and caused widespread, elevated PM2.5 concentrations across the province. Further information and analyses are provided in Wildfire smoke events in Ontario, 2023.
A summary of the 2023 PM2.5 annual statistics for individual roadside air monitoring stations is detailed in the Appendix: 2023 fine particulate matter (PM2.5) annual statistics for the roadside air monitoring network.
Ultrafine particles
Ultrafine particles are less than 0.1 µm in aerodynamic diameter and are mostly emitted from road traffic in urban environments. These tiny particles have larger surface areas per unit mass to absorb toxic chemicals and can also penetrate deep into the lungs.
Highlights
8-year trend
- Ultrafine particles across the roadside air monitoring network have decreased by 18%.
2023 results
- There is no AAQC for ultrafine particles.
8-year trends
Trend of ultrafine particles annual means across the roadside air monitoring network, 2016-2023
This is a line graph showing the trend of ultrafine particles annual mean concentrations from 2016 to 2023. The ultrafine particles annual mean concentrations within the network have decreased by 18% over this 8-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 8-year trend is based on data from three roadside air monitoring stations in Toronto.
- Ontario does not have an annual AAQC for ultrafine particles.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
The 8-year trend for ultrafine particles at individual roadside air monitoring stations in Ontario is presented in the Appendix: 8-year trend for ultrafine particles.
2023 results
Averaging time | Low range | High range | Number of sites with AAQC exceedances |
---|---|---|---|
Ultrafine particles 1-hour max | 80,180 particles/cm3 at Toronto North | 168,255 particles /cm3 at Toronto Hwy 401 | Not applicable |
Ultrafine particles 24-hour max | 16,501 particles/cm3 at Toronto Island | 84,078 particles /cm3 at Toronto Hwy 401 | Not applicable |
A summary of the 2023 ultrafine particles annual statistics for individual roadside air monitoring stations is detailed in the Appendix: 2023 ultrafine particles annual statistics.
Black carbon
Black carbon is a sooty black material produced through incomplete combustion processes. It is emitted from anthropogenic (e.g., engines and coal-fired power plants) and natural sources (e.g., wildfires). Black carbon comprises a significant portion of fine particulate matter and is linked to both climate warming and adverse health effects.
Highlights
8-year trends
- Black carbon concentrations across the roadside air monitoring network have decreased by 33%.
2023 results
- There is no AAQC for black carbon.
8-year trends
Trend of black carbon annual means across the roadside air monitoring network, 2016-2023
This is a line graph showing the trend of black carbon annual mean concentrations from 2016 to 2023 across the roadside air monitoring network. The black carbon annual mean concentrations within the network have decreased by 33% over this 8-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 8-year trend is based on data from 8 roadside air monitoring stations.
- Ontario does not have an annual AAQC for black carbon.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
The 8-year trend for black carbon at individual roadside air monitoring stations in Ontario is presented in the Appendix: 8-year trend for black carbon.
2023 results
Averaging time | Low range | High range | Number of sites with AAQC exceedances |
---|---|---|---|
Black carbon 1-hour max | 4.64 µg/m3 at Windsor Downtown | 21.42 µg/m3 at Toronto Island | Not applicable |
lack carbon 24-hour max | 1.67 µg/m3 at Hamilton Downtown | 4.62 µg/m3 at Toronto Hwy 401 | Not applicable |
A summary of the 2023 black carbon annual statistics for individual roadside air monitoring stations is detailed in the Appendix: 2023 black carbon annual statistics.
Heavy metals in PM2.5
Heavy metals are a loose term used to refer to naturally occurring trace elements, including metals that reside lower in the Periodic Table of Elements. Heavy metals in PM2.5 are often associated with industrial processes, vehicle emissions, and various human activities. When inhaled, these airborne particles can accumulate in the body over time and have adverse health effects, particularly when exposure levels are high or prolonged. The ministry measures 24 heavy metals in PM2.5, of which six select metals are presented below since they are often measured above their respective detection limits.
Highlights
8-year trends
Across the roadside air monitoring network:
- Ambient iron concentrations have increased by 48%.
- No trend for copper in ambient air.
- Ambient manganese concentrations have decreased by 28%.
- Ambient lead concentrations have decreased by 26%.
- Ambient selenium concentrations have increased by 21%.
- Ambient zinc concentrations decreased by 35%.
2023 results
- No exceedances of the 24-hour AAQC for manganese in PM2.5.
- There are no AAQC for iron, copper, lead, selenium and zinc in PM2.5.
8-year trends
Trend of iron in PM2.5 annual means across the roadside air monitoring network, 2016-2023
This is a line graph showing the trend of iron in PM2.5 annual mean concentrations from 2016 to 2023 across the roadside air monitoring network. Iron in PM2.5 annual mean concentrations increased by 48% over this 8-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 8-year trend is based on data from 2 roadside air monitoring stations.
- Ontario does not have an annual AAQC for iron in PM2.5.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
Trend of copper in PM2.5 annual means across the roadside air monitoring network, 2016-2023
This is a line graph showing the trend of copper in PM2.5 annual mean concentrations from 2016 to 2023 across the roadside air monitoring network. There was no trend over this 8-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 8-year trend is based on data from 2 roadside air monitoring stations.
- Ontario does not have an annual AAQC for copper in PM2.5.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
Trend of manganese in PM2.5 annual means across the roadside air monitoring network, 2016-2023
This is a line graph showing the trend of manganese in PM2.5 annual mean concentrations from 2016 to 2023 across the roadside air monitoring network. Manganese in PM2.5 annual mean concentrations decreased by 28% over this 8-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 8-year trend is based on data from 2 roadside air monitoring stations.
- Ontario does not have an annual AAQC for manganese in PM2.5.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
Trend of lead in PM2.5 annual means across the roadside air monitoring network, 2016-2023
This is a line graph showing the trend of lead in PM2.5 annual mean concentrations from 2016 to 2023 across the roadside air monitoring network. Lead in PM2.5 annual mean concentrations decreased by 26% over this 8-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 8-year trend is based on data from 2 roadside air monitoring stations.
- Ontario does not have an annual AAQC for lead in PM2.5.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
Trend of selenium in PM2.5 annual means across the roadside air monitoring network, 2016-2023
This is a line graph showing the trend of selenium in PM2.5 annual mean concentrations from 2016 to 2023 across the roadside air monitoring network. Selenium in PM2.5 annual mean concentrations increased by 21% over this 8-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 8-year trend is based on data from 2 roadside air monitoring stations.
- Ontario does not have an annual AAQC for selenium in PM2.5.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
Trend of zinc in PM2.5 annual means across the roadside air monitoring network, 2016-2023
This is a line graph showing the trend of zinc in PM2.5 annual mean concentrations from 2016 to 2023 across the roadside air monitoring network. Zinc in PM2.5 annual mean concentrations decreased by 35% over this 8-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 8-year trend is based on data from 2 roadside research air monitoring stations.
- Ontario does not have an annual AAQC for zinc in PM2.5.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
The 8-year trend for heavy metals at individual roadside air monitoring stations in Ontario is presented in the Appendix: 8-year trend for iron in PM2.5; 8-year trend for copper in PM2.5; 8-year trend for manganese in PM2.5; 8-year trend for lead in PM2.5; 8-year trend for selenium in PM2.5; 8-year trend for zinc in PM2.5.
2023 results
Averaging time | Low range | High range | Number of sites with AAQC exceedances |
---|---|---|---|
Iron in PM2.5 1-hour max | 2,005.7 ng/m3 at Toronto Hwy 401 | 3,200.3 ng/m3 at Windsor West | Not applicable |
Iron in PM2.5 24-hour max | 417.6 ng/m3 at Windsor West | 741.7 ng/m3 at Toronto Hwy 401 | Not applicable |
Copper in PM2.5 1-hour max | 187.2 ng/m3 at Windsor West | 305.2 ng/m3 at Toronto Hwy 401 | Not applicable |
Copper in PM2.5 24-hour max | 18.3 ng/m3 at Windsor West | 55.7 ng/m3 at Toronto Hwy 401 | Not applicable |
Manganese in PM2.5 1-hour max | 45.0 ng/m3 at Toronto Hwy 401 | 114.7 ng/m3 at Windsor West | Not applicable |
Manganese in PM2.5 24-hour max | 12.8 ng/m3 at Toronto Hwy 401 | 22.1 ng/m3 at Windsor West | Not applicable |
Lead in PM2.5 1-hour max | 129.9 ng/m3 at Windsor West | 397.2 ng/m3 at Toronto Hwy 401 | Not applicable |
Lead in PM2.5 24-hour max | 17.2 ng/m3 at Windsor West | 22.4 ng/m3 at Toronto Hwy 401 | Not applicable |
Selenium in PM2.5 1-hour max | 26.64 ng/m3 at Windsor West | 130.90 ng/m3 at Toronto Hwy 401 | Not applicable |
Selenium in PM2.5 24-hour max | 3.84 ng/m3 at Windsor West | 10.32 ng/m3 at Toronto Hwy 401 | Not applicable |
Zinc in PM2.5 1-hour max | 607.8 ng/m3 at Windsor West | 947.5 ng/m3 at Toronto Hwy 401 | Not applicable |
Zinc in PM2.5 24-hour max | 108.3 ng/m3 at Windsor West | 202.6 ng/m3 at Toronto Hwy 401 | Not applicable |
A summary of the 2023 heavy metals in PM2.5 annual statistics for individual roadside air monitoring stations is detailed in the Appendix: 2023 iron in PM2.5 annual statistics; 2023 copper in PM2.5 annual statistics; 2023 manganese in PM2.5 annual statistics; 2023 lead in PM2.5 annual statistics; 2023 selenium in PM2.5 annual statistics; and 2023 zinc in PM2.5 annual statistics.
Major components in PM2.5
Major components in PM2.5, with the exception of black carbon and metals, are the parts of tiny particles that can change or evaporate when exposed to heat (also known as non-refractory species in PM2.5). In the air, these include organic compounds, sulphate, nitrate and ammonium compounds. Vehicle emissions and industry are major sources of these components which can affect human health.
The ministry monitors major components in PM2.5 at the Toronto Hwy 401 air monitoring station, however, due to technical difficulties, there were insufficient data in 2023 to calculate a valid annual mean. The Toronto Hwy 401 air monitoring station measures five major components in PM2.5, of which four components are presented since chloride is mostly below its detection limit.
Highlights
8-year trends
- No trend for organics in PM2.5
- No trend for sulphate in PM2.5
- Nitrate in PM2.5 has decreased 25%
- No trend for ammonium in PM2.5
2023 results
- There are no AAQC for major components in PM2.5, such as organics, sulphate, nitrate and ammonium.
8-year trends
Trend of organics in PM2.5 at Toronto Hwy 401, 2016-2023
This is a line graph showing the trend of organics in PM2.5 annual mean concentrations from 2016 to 2023 at the Toronto Hwy 401 roadside air monitoring station. There was no trend over this 8-year period.
Note:
- Ontario does not have an annual AAQC for organics in PM2.5.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
Trend of sulphate in PM2.5 at Toronto Hwy 401, 2016-2023
This is a line graph showing the trend of sulphate in PM2.5 annual mean concentrations from 2016 to 2023 at the Toronto Hwy 401 roadside air monitoring station. There was no trend over this 8-year period.
Note:
- Ontario does not have an annual AAQC for sulphate in PM2.5.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
Trend of nitrate in PM2.5 at Toronto Hwy 401, 2016-2023
This is a line graph showing the trend of nitrate in PM2.5 annual mean concentrations from 2016 to 2023 at the Toronto Hwy 401 roadside air monitoring station. Nitrate in PM2.5 annual mean concentrations decreased by 25% over this 8-year period.
Note:
- Ontario does not have an annual AAQC for nitrate in PM2.5.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
Trend of ammonium in PM2.5 at Toronto Hwy 401, 2016-2023
This is a line graph showing the trend of ammonium in PM2.5 annual mean concentrations from 2016 to 2023 at the Toronto Hwy 401 roadside air monitoring station. There was no trend over this 8-year period.
Note:
- Ontario does not have an annual AAQC for ammonium in PM2.5.
- Air quality in Ontario can vary from year to year due to a variety of factors including pollutant emissions, weather, natural events such as wildfires, and the long-range transport of air pollutants from the United States and elsewhere. Long term trends are thus a better reflection of any improvements or a deterioration in air quality over time versus year over year changes.
Relative distribution of major components in PM2.5 at Toronto Hwy 401, 2016-2023
This is a stacked column chart showing the relative distribution of major components in PM2.5 based on annual mean concentrations from 2016 to 2023 at the Toronto Hwy 401 roadside air monitoring station. Relative contribution of PM2.5 components varied from year to year with the organic component representing the largest contribution across all years; however, data reporting requirements were not met in 2023 to calculate annual mean concentrations.
The 8-year trends for the four major components in PM2.5 monitored at the Toronto Hwy 401 roadside air monitoring station in Ontario are presented in the Appendix: 8-year trend for organics in PM2.5; 8-year trend for sulphate in PM2.5; 8-year trend for nitrate in PM2.5; 8-year trend for ammonium in PM2.5.
2023 results
Averaging time | Low range | High range | Number of sites with AAQC exceedances |
---|---|---|---|
Organics in PM2.5 1-hour max | 95.6 µg/m3 at Toronto Hwy 401 | 174.2 µg/m3 at Windsor West | Not applicable |
Organics in PM2.5 24-hour max | 36.59 µg/m3 at Toronto Hwy 401 | 96.39 µg/m3 at Windsor West | Not applicable |
Sulphate in PM2.5 1-hour max | 3.3 µg/m3 at Windsor West | 12.5 µg/m3 at Toronto Hwy 401 | Not applicable |
Sulphate in PM2.5 24-hour max | 1.07 µg/m3 at Windsor West | 8.04 µg/m3 at Toronto Hwy 401 | Not applicable |
itrate in PM2.5 1-hour max | 7.5 µg/m3 at Windsor West | 19.0 µg/m3 at Toronto Hwy 401 | Not applicable |
Nitrate in PM2.5 24-hour max | 4.34 µg/m3 at Windsor West | 10.97 µg/m3 at Toronto Hwy 401 | Not applicable |
Ammonium in PM2.5 1-hour max | 3.0 µg/m3 at Windsor West | 11.5 µg/m3 at Toronto Hwy 401 | Not applicable |
Ammonium in PM2.5 24-hour max | 1.63 µg/m3 at Windsor West | 6.72 µg/m3 at Toronto Hwy 401 | Not applicable |
A summary of the 2023 annual statistics for major components in PM2.5 at the Windsor West and Toronto Hwy 401 roadside air monitoring stations is detailed in the Appendix: 2023 organics in PM2.5 annual statistics; 2023 sulphate in PM2.5 annual statistics; 2023 nitrate in PM2.5 annual statistics, 2023 ammonium in PM2.5 annual statistics.