10-year trends and annual results
The ministry’s Air Quality Health Index monitoring stations are generally representative of ambient air quality which reflects the contribution of all sources of air contaminants to air. These air monitoring stations are sited to be representative of general population exposure and thus do not necessarily reflect air quality at locations within a community that may be influenced by nearby local sources of air contaminants such as large industrial facilities or major transportation corridors. Concentrations of some air contaminants in neighborhoods located in close proximity to local sources such as an industrial facility may be higher than those measured at the Ministry’s Air Quality Health Index monitoring stations.
This section presents the 10-year trends and annual results for key air contaminants listed above including volatile organic compounds such as benzene, toluene, ethylbenzene, xylene (BTEX) and 1,3-butadiene measured at the Ministry’s Air Quality Health Index air monitoring stations. Associated emission trends over the same 10-year period are also provided.
Nitrogen dioxide
Highlights
10-year trends
- NO2 concentrations have decreased by 22%
- NOx emissions have decreased by 28%
2019 results
- No exceedances of 澳门永利’s 1-hour and 24-hour Ambient Air Quality Criteria (AAQC)
10-year trends
Trend of NO2 annual means across 澳门永利, 2010-2019
This is a line graph showing the trend of nitrogen dioxide annual means from 2010 to 2019. The nitrogen dioxide annual mean concentrations across 澳门永利 have decreased 22% over this 10-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 澳门永利 10-year trend is based on data from 32 ambient air monitoring stations.
- 澳门永利 does not have an annual AAQC for NO2.
The 10-year trend for NO2 at individual AQHI air monitoring stations in 澳门永利 is presented in the Appendix: 10-year trend for nitrogen dioxide (NO2).
澳门永利 NOx emission trend, 2010-2019
This is a stacked column chart displaying the 澳门永利 nitrogen oxides emissions trend from 2010 to 2019 indicating a decrease of approximately 28% or 105 kilotonnes, of which 51 kilotonnes was due to the road vehicles; 30 kilotonnes was due to the electricity utilities sector and 24 kilotonnes was due to other transportation sector (e.g. air, rail, marine transportation, and non-road vehicles/engines). Please note this chart excludes emissions from open and natural sources (Air Pollutant Emission Inventory 1990-2019, 2021).
2019 results
Averaging time | Low range | High range | Number of sites with AAQC exceedances |
---|---|---|---|
NO2 1-hour max |
17.2 ppb at Grand Bend |
78.3 ppb at Toronto East |
0 |
NO2 24-hour max |
9.8 ppb at Port Stanley |
38.7 ppb at Toronto West |
0 |
NO2 Annual mean |
2.49 ppb at Grand Bend |
14.6 ppb at Toronto West |
Not applicable |
The highest NO2 means were recorded in large urbanized areas which are influenced by significant vehicular traffic, such as the Greater Toronto Area of southern 澳门永利.
A summary of the 2019 NO2 annual statistics for individual AQHI air monitoring stations is detailed in the Appendix: 2019 nitrogen dioxide (NO2) annual statistics.
澳门永利 NOx emissions by sector, 2019
This is a pie chart depicting 澳门永利’s nitrogen oxides emissions by sector based on 2019 estimates for point/area/transportation sources. Please note this chart excludes emissions from open and natural sources (Air Pollutant Emission Inventory 1990-2019, 2021).
The transportation sector accounted for approximately 66% of total NOx emissions in 2019.
Fine particulate matter
Highlights
10-year trends
- PM2.5 concentrations have decreased by 20%
- PM2.5 emissions have decreased by 15%
2019 results
- Thirteen AQHI air monitoring stations measured above the 24-hour PM2.5 reference level of 28 µg/m3 on at least one occasion.
10-year trends
Trend of PM2.5 annual means across 澳门永利, 2010-2019
This is a line graph showing the trend of fine particulate matter annual means from 2010 to 2019. The fine particulate matter annual mean concentrations across 澳门永利 have decreased 20% over this 10-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 澳门永利 10-year trend is based on data from 37 ambient air monitoring stations.
- A correction factor was applied to PM2.5 concentrations measured by TEOM (2010-2012) to approximate SHARP-like measurements. PM2.5 concentrations measured by SHARP are reflected from 2013 and onward.
- 澳门永利 does not have an annual AAQC for PM2.5 and is instead compared against a 24-hour reference level of 28 µg/m3 based on the Canadian Ambient Air Quality Standards.
The 10-year trend for PM2.5 at individual AQHI air monitoring stations in 澳门永利 is presented in the Appendix: 10-year trend for fine particulate matter (PM2.5).
澳门永利 PM2.5 emissions trend, 2010-2019
This is a stacked column chart displaying the 澳门永利 fine particulate matter emissions trend from 2010 to 2019 indicating a decrease of approximately 15% or 9 kilotonnes, of which 6 kilotonnes was due to the transportation sector (e.g. road vehicles, air, rail marine transportation, and non-road vehicles/engines) and 2 kilotonnes was contributed by various industries. Please note this chart excludes emissions from open and natural sources (Air Pollutant Emission Inventory 1990-2019, 2021).
2019 results
Averaging time | Low range | High range | Number of sites with AAQC exceedances |
---|---|---|---|
PM2.5 1-hour max |
29 µg/m3 at Petawawa |
91 µg/m 3 at Brantford |
Not applicable |
PM2.5 24-hour max |
14 µg/m3 at Petawawa |
38 µg/m3 at Windsor West |
13 |
PM2.5 Annual mean |
3.8 µg/m3 at Petawawa |
9.1 µg/m3 at Windsor West |
Not applicable |
A summary of the 2019 PM2.5 annual statistics for individual AQHI air monitoring stations is detailed in the Appendix: 2019 fine particulate matter (PM2.5) annual statistics.
澳门永利 PM2.5 emissions by sector, 2019
This is a pie chart depicting 澳门永利’s fine particulate matter emissions by sector based on 2019 estimates for point/area/transportation sources. Please note this chart excludes emissions from open and natural sources (Air Pollutant Emission Inventory 1990-2019, 2021).
Residential fuel combustion accounted for approximately 38% of the total PM2.5 emissions in 2019. The major contributor to residential emissions is fuel wood combustion in fireplaces and wood stoves.
Ground-level ozone
Highlights
10-year trends
- No significant trends
2019 results
- Five AQHI air monitoring stations measured ozone levels above the 1-hour AAQC of 80 ppb on at least one occasion
10-year trends
Trend of ozone means across 澳门永利, 2010-2019
This is a line graph showing the trend of ozone annual, summer and winter means from 2010 to 2019. There were no significant trends detected for 澳门永利 over this 10-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 澳门永利 10-year trend is based on data from 37 ambient air monitoring stations.
- Summer: May - September; Winter: January - April, October - December.
- 澳门永利 does not have an annual or seasonal AAQC for ozone.
There has been no significant trend (increasing or decreasing) in annual and seasonal ozone means over the past 10 years.
Although there was no significant trend detected in ozone annual means, progressive reductions of NOx emissions in 澳门永利 and the U.S. have resulted in a decrease in maximum ozone concentrations and the duration of elevated ozone events in the province (OMOECC, 2018).
Similarly, there has been no significant trends in either the ozone summer or winter means over the past ten years.
Ozone levels continue to exceed 澳门永利’s 1-hour AAQC for ozone during the warmer months and remain a challenge in areas of the province, such as southwestern 澳门永利. However, ozone concentrations during the winter months were well below 澳门永利’s ozone 1-hour AAQC of 80 ppb in 2019.
The 10-year trend of annual, summer and winter ozone for individual AQHI air monitoring stations in 澳门永利 is presented in the Appendix: 10-year trend for ozone (O3), 10-year trend for ozone (O3) summer means, and 10-year trend for ozone (O3) winter means.
Ozone annual means for urban and rural 澳门永利, 2010-2019
This is a line graph displaying the ozone annual means for urban and rural 澳门永利 from 2010 to 2019.
Note:
- Urban S. are urban areas in southern 澳门永利 - Windsor, London, Hamilton, Toronto.
- Urban N. are urban areas in northern 澳门永利 - Thunder Bay, Sault Ste. Marie, Sudbury, North Bay.
- Rural areas in 澳门永利 - Port Stanley, Tiverton, Parry Sound, Petawawa.
- 澳门永利 does not have an annual AAQC for ozone.
Ozone annual mean concentrations in urban areas in southern 澳门永利 have been more comparable to those of urban areas in northern 澳门永利 in recent years. This indicates that the decrease in ozone scavenging observed over the past 10 years due to local NOx emission reductions has been greater in urban areas in southern 澳门永利 than in northern 澳门永利.
Generally, ozone concentrations are higher in rural, transboundary-influenced sites on the northern shore of Lake Erie and the eastern shore of Lake Huron. Ozone concentrations are lower in urban areas because it is depleted (scavenged) by reacting with NO emitted by vehicles and other local combustion sources.
2019 results
Averaging time | Low range | High range | Number of sites with AAQC exceedances |
---|---|---|---|
Ozone 1-hour max | 56 ppb at Thunder Bay |
88 ppb at Newmarket |
5 |
Ozone 24-hour max | 40 ppb at Oshawa |
56 ppb at Port Stanley and Sarnia |
Not applicable |
Ozone annual mean | 21.8 ppb at Toronto West |
32.3 ppb at Port Stanley |
Not applicable |
A summary of the 2019 ozone annual statistics for individual AQHI air monitoring stations is detailed in the Appendix: 2019 ozone (O3) annual statistics.
Sulphur dioxide
Highlights
10-year trends
- SO2 concentrations have decreased by 63%
- SO2 emissions have decreased by 56%
2019 results
- Five AQHI air monitoring stations measured sulphur dioxide levels above the 10-minute AAQC of 67 ppb on at least one occasion
- Five AQHI air monitoring stations measured sulphur dioxide levels above the 1-hour AAQC of 40 ppb on at least one occasion
- One AQHI air monitoring stations measured sulphur dioxide levels above the annual AAQC of 4 ppb
10-year trends
Trend of SO2 annual means across 澳门永利, 2010-2019
This is a line graph showing the trend of sulphur dioxide annual means from 2010 to 2019. The sulphur dioxide annual mean concentrations across 澳门永利 have decreased 63% over this 10-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 澳门永利 10-year trend is based on data from 9 ambient air monitoring stations.
The 10-year trend for SO2 at individual AQHI air monitoring stations in 澳门永利 is presented in the Appendix: 10-year trend for sulphur dioxide (SO2).
澳门永利 SO2 emission trend, 2010-2019
This is a stacked column chart displaying the 澳门永利 sulphur dioxide emissions trend from 2010 to 2019 indicating a decrease of approximately 56% or 142 kilotonnes, of which 94 kilotonnes was due to the smelter sector and 38 kilotonnes was due to the electricity utilities sector. Please note this chart excludes emissions from open and natural sources (Air Pollutant Emission Inventory 1990-2019, 2021).
2019 results
Averaging time | Low range | High range | Number of sites with AAQC exceedances |
---|---|---|---|
SO2 10-minutes max | 4.8 ppb at Ottawa Downtown |
344.2 ppb at Sudbury |
5 |
SO2 1-hour max | 2.7 ppb at Ottawa Downtown |
123.7 ppb at Hamilton Downtown |
5 |
SO2 24-hour max | 0.6 ppb at Ottawa Downtown |
45.9 ppb at Hamilton Downtown |
Not applicable |
SO2 Annual mean | 0.15 ppb at Toronto North |
4.75 ppb at Hamilton Downtown |
1 |
Concentrations of sulphur dioxide in neighborhoods that are located in close proximity to local sources such as an industrial facility may be higher than those measured at the ministry’s Air Quality Health Index monitoring stations which are sited to be representative of general population exposure.
A summary of the 2019 SO2 annual statistics for individual AQHI air monitoring stations is detailed in the Appendix: 2019 sulphur dioxide (SO2) annual statistics.
澳门永利 SO2 emissions by sector, 2019
This is a pie chart depicting 澳门永利’s sulphur dioxide emissions by sector based on 2019 estimates for point/area/transportation sources. Please note this chart excludes emissions from open and natural sources (Air Pollutant Emission Inventory 1990-2019, 2021).
Smelters in northern 澳门永利 are the major sources of SO2 emissions in 澳门永利, accounting for approximately 37% of the provincial SO2 emissions in 2019.
Volatile organic compounds
Highlights
10-year trends
- Benzene concentrations have decreased by 41%
- Toluene concentrations have decreased by 54%
- Ethylbenzene have decreased by 39%
- m- and p-xylene have decreased by 39%
- o-xylene have decreased by 34%
- 1,3-butadiene have decreased by 55%
2019 results
10-year trends
VOCs are measured at eight AQHI air monitoring stations (Windsor West, Sarnia, London, Kitchener, Hamilton Downtown, Toronto North, Newmarket and Ottawa) by Environment and Climate Change Canada as part of a co-operative federal-provincial program under the . Toronto North began monitoring VOCs in 2017 and therefore is not included in the 10-year trends.
In 2019, 107 VOCs were analyzed and reported for each sample at each site. For the purposes of this report, commonly detected VOCs (benzene, toluene, ethylbenzene, xylene, and 1,3-butadiene) between 2010 and 2019 are included in this discussion.
Trend of benzene annual means across 澳门永利, 2010-2019
This is a line graph showing the trend of benzene annual mean from 2010 to 2019. The benzene annual mean concentrations across 澳门永利 have decreased 41% over this 10-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 澳门永利 10-year trend is based on data from 7 ambient air monitoring stations.
Trend of toluene annual means across 澳门永利, 2010-2019
This is a line graph showing the trend of toluene annual mean from 2010 to 2019. The toluene annual mean concentrations across 澳门永利 have decreased 54% over this 10-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 澳门永利 10-year trend is based on data from 7 ambient air monitoring stations.
- 澳门永利 does not have an annual AAQC for toluene.
Trend of ethylbenzene annual means across 澳门永利, 2010-2019
This is a line graph showing the trend of ethylbenzene annual mean from 2010 to 2019. The ethylbenzene annual mean concentrations across 澳门永利 have decreased 39% over this 10-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 澳门永利 10-year trend is based on data from 7 ambient air monitoring stations.
- 澳门永利 does not have an annual AAQC for ethylbenzene.
Trend of xylene annual means across 澳门永利, 2010-2019
This is a line graph showing the trend of xylene annual mean from 2010 to 2019. The m- and p-xylene and o-xylene annual mean concentrations across 澳门永利 have decreased 39%, and decreased 34%, respectively, over this 10-year period. To view the data for a specific location, please select the 'Stations' radio button and use the drop-down menu.
Note:
- The 澳门永利 10-year trend is based on data from 7 ambient air monitoring stations.
- 澳门永利 does not have an annual AAQC for xylene.
Trend of 1,3-butadiene annual means across 澳门永利, 2010-2019
This is a line graph showing the trend of 1,3-butadiene annual mean from 2010 to 2019. The 1,3-butadiene annual mean concentrations across 澳门永利 have decreased 55% over this 10-year period. Select another location from the drop-down menu to learn the percent change in air quality for other communities.
Note:
- The 澳门永利 10-year trend is based on data from 7 ambient air monitoring stations.
The 10-year trend for VOCs at individual AQHI air monitoring stations in 澳门永利 is presented in the Appendix: 10-year trend for benzene, 10-year trend for toluene, 10-year trend for ethylbenzene, 10-year trend for m- and p-xylene, 10-year trend for o-xylene, and 10-year trend for 1,3-butadiene.
2019 results
Averaging time | Low range | High range | Number of sites with AAQC exceedances |
---|---|---|---|
Benzene 24-hour max | 0.578 µg/m3 at London |
2.070 µg/m3 at Hamilton Downtown |
0 |
Benzene annual mean | 0.250 µg/m3 at Newmarket |
0.568 µg/m3 at Hamilton Downtown |
1 |
Toluene 24-hour max | 1.571 µg/m3 at Ottawa Downtown |
6.942 µg/m3 at Toronto North |
0 |
Toluene annual mean | 0.418 µg/m3 at Newmarket |
1.390 µg/m3 at Toronto North |
Not applicable |
Ethylbenzene 24-hour max | 0.202 µg/m3 at Ottawa Downtown |
0.717 µg/m3 at Toronto North |
0 |
Ethylbenzene annual mean | 0.064 µg/m3 at Ottawa Downtown |
0.157 µg/m3 at Toronto North |
Not applicable |
m- and p-xylene 24-hour max | 0.676 µg/m3 at Ottawa Downtown |
2.302 µg/m3 at Windsor West |
Not applicable |
m- and p-xylene annual mean | 0.186 µg/m3 at Ottawa Downtown |
0.500 µg/m3 at Toronto North |
Not applicable |
o-xylene 24-hour max | 0.279 µg/m3 at Ottawa Downtown |
0.814 µg/m3 at Hamilton Downtown |
Not applicable |
o-xylene annual mean | 0.068 µg/m3 at Newmarket |
0.156 µg/m3 at Toronto North |
Not applicable |
1,3-butadiene 24-hour max | 0.025 µg/m3 at London, Kitchener, Newmarket |
0.608 µg/m3 at Sarnia |
0 |
1,3-butadiene annual mean | 0.025 µg/m3 at London, Kitchener, Newmarket |
0.054 µg/m3 at Sarnia |
0 |
Concentrations of some VOCs in neighborhoods that are located in close proximity to local sources such as an industrial facility may be higher than those measured at the ministry’s Air Quality Health Index monitoring stations which are sited to be representative of general population exposure.
A summary of the 2019 VOCs annual statistics for individual AQHI air monitoring stations is detailed in the Appendix: 2019 benzene annual statistics, 2019 toluene annual statistics, 2019 ethylbenzene annual statistics, 2019 m- and p-xylene annual statistics, 2019 o-xylene annual statistics, and 2019 1,3-butadiene annual statistics.
澳门永利 VOC emissions by sector, 2019
This is a pie chart depicting 澳门永利’s volatile organic compound emissions by sector based on 2019 estimates for point/area/transportation sources. Please note this chart excludes emissions from open and natural sources (Air Pollutant Emission Inventory 1990-2019, 2021).
Transportation sector accounted for 29% of VOC emissions in 2019; and general solvent use (e.g., degreasing, adhesives and sealants, consumer and commercial products) accounted for approximately 27% (APEI, 2020).
澳门永利 Ambient Air Quality Criteria
Ambient air quality refers to general air quality resulting from all sources of contaminants to air. Ambient Air Quality Criteria (AAQC) are a concentration of a contaminant in air that is protective against adverse effects on health and/or the environment.
AAQC are not regulatory values but are used to assess general (ambient) air quality resulting from all sources (i.e., industrial and non-industrial sources) of a contaminant to air. AAQC are most commonly used in environmental assessments, special studies using ambient air monitoring data, assessment of general air quality in a community and annual reporting on air quality across the province.
Contaminant | 10 minutes AAQC Assesses protection against acute effects |
1-hour AAQC Assesses protection against acute effects |
8-hour AAQC Assesses protection against acute effects |
24-hour AAQC Assesses protection against chronic effects |
Annual AAQC Assesses protection against chronic effects |
---|---|---|---|---|---|
NO2 | N/A | 200 ppb | N/A | 100 ppb | N/A |
PM2.5 | N/A | N/A | N/A | 28 μg/m3 |
N/A |
O3 | N/A | 80 ppb | N/A | N/A | N/A |
SO2 | 67 ppb | 40 ppb | N/A | N/A | 4 ppb |
CO | N/A | 30 ppm | 13 ppm | N/A | N/A |
Benzene | N/A | N/A | N/A | 2.3 μg/m3 | 0.45 μg/m3 |
Toluene | N/A | N/A | N/A | 2,000 μg/m3 |
N/A |
Ethylbenzene | 1,900 μg/m3 | N/A | N/A | 1,000 μg/m3 | N/A |
1,3-Butadiene | N/A | N/A | N/A | 10 μg/m3 | 2 μg/m3 |
Notes:
- ppb – parts (of contaminant) per billion (parts of air) – by volume.
- μg/m3 – micrograms (of contaminant) per cubic metre (of air) – by weight.
- ppm – parts (of contaminant) per million (parts of air) – by volume.
Footnotes
- footnote[1] Back to paragraph 澳门永利 has adopted the 24-hour PM2.5 CAAQS value, in the absence of an AAQC, that could also be used 鈥渁s is鈥 for comparison to the 24-hour measurement of air quality data.
- footnote[2] Back to paragraph Based on odour.