2012 Air Quality Report Highlights

The 2012 air quality report marks 42 years of long-term reporting on the state of air quality in Ontario. This report summarizes province- wide trends for key airborne pollutants affecting Ontario’s air quality.

Overall, air quality has improved significantly over the past 10 years, especially for nitrogen dioxide (NO2), sulphur dioxide (SO2) and carbon monoxide (CO) – pollutants emitted by vehicles and industry, as well as fine particulate matter (PM2.5), which may be emitted directly into the atmosphere as a by-product of fuel combustion or it may be formed indirectly in the atmosphere through a series of complex chemical reactions.

Ozone is a secondary pollutant formed when nitrogen oxides (NOX) and volatile organic compounds (VOCs) react in the presence of sunlight. Ozone annual means have increased by 8 per cent from 2003 to 2012; however, ozone summer means have remained constant over the same period.

Emissions of nitrogen oxides (NOX), CO and SO2 continue to decrease due in part to Ontario’s air quality initiatives such as the phase-out of coal-fired generating stations, emissions trading regulations (O. Reg. 397/01 and O. Reg. 194/05), emissions controls at Ontario smelters, and Drive Clean emissions testing, which supports the federal vehicle emission standards and lower sulphur content in transportation fuels.

Decreasing Provincial Ambient Concentrations (2003 - 2012)
NO2 decreased 43%
SO2 decreased 52%
CO decreased 43%
PM2.5 decreased 31%
Decreasing Provincial Emmissions (2002 - 2011)
NOX decreased 39%
SO2 decreased 55%
CO decreased 22%
PM2.5 decreased 25%

For more information, visit the Ontario’s Air Quality web site.

1.0 Introduction

This annual report, the 42nd in a series, summarizes the state of ambient air quality in Ontario during 2012 and examines 10-year trends. It reports on the measured levels of six common air pollutants: ground-level ozone (O3), fine particulate matter (PM2.5), nitrogen dioxide (NO2), carbon monoxide (CO), sulphur dioxide (SO2) and total reduced sulphur (TRS) compounds. This report also provides an overview of the Air Quality Index (AQI) and Smog Alert programs. Annual statistics, as well as 10- and 20-year trends of ambient air quality data are in the attached appendix.

Ontario continues to benefit from one of the most comprehensive air monitoring systems in North America, comprised of 40 monitoring sites across the province that undergo regularly scheduled maintenance and strict data quality assurance and quality control (QA/QC) procedures to ensure a high standard of data quality and data completeness. The data, which are collected continuously at these sites, are used to determine the current state of air quality and are reported every hour on Ontario’s Air Quality web site.

2.0 Ground-Level Ozone (O3)

Ground-level ozone is a gas formed when nitrogen oxides (NOX) and volatile organic compounds (VOCs) react in the presence of sunlight. While ozone at ground level is a significant environmental and health concern, the naturally occurring ozone in the stratosphere, 10 to 40 kilometres above the Earth’s surface, is beneficial as it shields the earth from harmful ultraviolet radiation.

Ozone is a colourless, odourless gas at typical ambient concentrations, and is a major component of smog. Ozone is not generally emitted directly into the atmosphere; the formation and transport of ozone is strongly dependent on meteorological conditions and emissions of chemical precursors, particularly NOX and VOCs. Changing weather patterns contribute to differences in ozone concentrations hour-to-hour, day-to-day, season-to-season, and year-to-year. In Ontario, the highest concentrations of ground-level ozone are typically recorded on hot and sunny days from mainly May to September, between noon and early evening.

Figure 1 shows the estimates of Ontario’s VOCs emissions from point, area and transportation sources. Transportation sectors accounted for approximately 35 per cent of VOCs emissions and the second largest source was general solvent use accounting for approximately 27 per cent. Figure 2 shows the estimates for Ontario’s NOX emissions from point, area and transportation sources. The transportation sectors accounted for approximately 72 per cent of NOX  emissions (NPRI, 2013).

Ozone irritates the respiratory tract and eyes. Exposure to ozone in sensitive people can result in chest tightness, coughing and wheezing. Children who are active outdoors during the summer, when ozone levels are highest, are particularly at risk. Individuals with pre-existing respiratory disorders, such as asthma and chronic obstructive pulmonary disease (COPD), are also at risk. Ozone is associated with increased hospital admissions and premature deaths. Ozone also causes many losses in agricultural crops each year in Ontario, with visible leaf damage in many crops, garden plants and trees, especially during the summer months.

Figure 1: Ontario VOCs Emissions by Sector (2011 Estimates for Point/Area/Transportation Sources)

Figure 1 shows  the estimates of Ontario’s Volatile Organic Compound emissions from point, area and transportation sources.

Note: Excludes emissions from open and natural sources.

Figure 2: Ontario Nitrogen Oxides Emissions by Sector (2011 Estimates for Point/Area/Transportation Sources)

Figure 2 shows the estimates for Ontario’s nitrogen oxide emissions from point, area and transportation sources.

Note: Excludes emissions from open and natural sources.

In 2012, ozone was monitored at the ministry’s 40 AQI sites. The highest annual mean was
33.2 parts per billion (ppb), measured at Grand Bend, a transboundary-influenced site on
the eastern shore of Lake Huron. The lowest annual mean, 22.3 ppb, was measured at Toronto West, an urban site located near a major transportation corridor, Highway 401, and directly impacted by local nitric oxide (NO) emissions from vehicles. Generally, ozone concentrations are lower in urban areas because ozone is depleted by reacting with NO emitted by vehicles and other local combustion sources.

Ground-level ozone concentrations continued to exceed the provincial one-hour Ambient Air Quality Criterion (AAQC) of 80 ppb at 34 sites in 2012. The maximum one-hour ozone concentrations ranged from 74 ppb recorded in Thunder Bay, to 128 ppb recorded in Windsor. Ontario’s one-hour AAQC for ozone was exceeded the most often at Grand Bend on 109 occasions. The geographical distribution of one-hour ozone exceedances across the province are shown in Figure 3.

Figure 3: Geographical Distrubution of One-Hour Ozone Exceedances Across Ontario in 2012

The geographical distribution of one-hour ozone exceedances across the province.

Generally, ozone exceedances are greater in southwestern Ontario, on the eastern shore of Lake Huron and on the northern shore of Lake Erie, more so than over central and eastern Ontario. As stated in the Transboundary Air Pollution in Ontario report, elevated ozone levels in southwestern Ontario are generally attributed to the long-range transport of pollutants from the United States. Transboundary air pollution is combined with local emissions of smog-related pollutants, and can impact various areas of the province during a smog episode (Yap et al., 2005).

As referenced in the Guidance Document on Achievement   Determination (GDAD), the Canada-wide Standard (CWS) for ozone is 65 ppb, eight-hour running average time, based on the 4th  highest annual ambient measurement averaged over three consecutive years. Of the 40 ambient air quality monitoring stations, 21 meet the requirements outlined in the GDAD (Canadian Council of Ministers of the Environment, 2007). In 2012, only two of the 21 CWS designated sites, Ottawa and Thunder Bay, met the CWS  of 65 ppb for ozone. Table A19 of the Appendix provides a complete summary of reported CWS metrics since 2005.

The ozone annual means in Figure 4 display an increasing trend of 8 per cent for the 10-year period from 2003 to 2012. The trend of ozone summer means and ozone winter means are shown in Figure 5. The ozone summer means trend remained constant from 2003 to 2012, whereas the ozone winter means have increased by 16 per cent over the same 10- year period. The increase in the ozone winter means are mainly attributed to the rising global background concentrations which in turn drives the increasing trend of ozone annual means.

Figure 4: Trend of Ozone Annual Means Across Ontario (2003-2012)

The ozone annual means in Figure 4 display an increasing trend of 8 per cent for the 10-year period from 2003 to 2012.

Note: Ten-year trend is a composite annual mean based on data from 37 monitoring sites.

Figure 5: Trend of Ozone Summer and Winter Means Across Ontario (2003-2012)

The trend of ozone summer means and ozone winter means are shown in Figure 5. The ozone summer means trend remained  constant from 2003 to  2012, whereas the ozone winter means  have increased by 16 per cent over the same 10-year period.

Note: Ten-year trends are a composite means for the summer and winter months based on data from 37 monitoring sites. Summer: May - September; Winter January - April, October - December.

3.0 Fine Particulate Matter (PM2.5)

Airborne particulate is the general term used to describe a mixture of microscopic solid particles and liquid droplets suspended in air. Particulate matter is classified according to its aerodynamic size, mainly due to the different health effects associated with particles of different diameters. Fine particulate matter, denoted as PM2.5, refers to respirable particles that are less than 2.5 microns in diameter, approximately 30 times smaller than the average diameter of a human hair. Due to their small size, they can penetrate deep into the lungs.

Particulate matter includes aerosols, smoke, fumes, dust, fly ash and pollen. Its composition is complex and varies with origin, residence time in the atmosphere, time of year and environmental conditions. Major components of PM2.5 in Ontario are typically nitrates, sulphates, organic matter and particle-bound water. Higher nitrate levels are common in the cooler months whereas sulphates are more elevated during warm temperatures. Fineparticulate matter may be emitted directly into the atmosphere as a by-product of fuel combustion or it may be formed indirectly in the atmosphere through a series of complex chemical reactions. Major sources of PM2.5 include motor vehicles, smelters, power plants, industrial facilities, residential fireplaces and wood stoves, agricultural burning and forest fires.

The 2011 estimates for Ontario’s PM2.5 emissions from point, area and transportation sources (excluding emissions from open and natural sources) indicate residential fuel combustion accounted for 40 per cent. The major contributor to residential emissions is fuel wood combustion in fireplaces and wood stoves. Industrial processes and transportation sectors accounted for 29 per cent and 24 per cent, respectively (NPRI, 2013).

The 2012 PM2.5 annual mean concentrations ranged from 3.6 µg/m3 in Petawawa to
10.2 µg/m3 in Sarnia. During periods of elevated concentrations of PM2.5 in Ontario, it is estimated that there are significant contributions from the U.S., specifically affecting border communities (Yap et al., 2005). The PM2.5 24-hour maximum concentrations ranged from 13 µg/m3 in Thunder Bay to 36 µg/m3 in Parry Sound. The PM2.5 24-hour maximum concentration in Parry Sound was recorded on July 22, 2012 due to forest fire smoke that originated in northern Manitoba and travelled over 600 kilometres. In 2012, four of the 40 sites exceeded Ontario’s 24-hour PM2.5 reference level of 30 µg/m3 on at least one occasion.

Similar to Ontario’s 24-hour PM2.5 reference level, the CWS for PM2.5 is also 30 µg/m3, 24-hour averaging time; however, as referenced in the GDAD, the CWS is based on the 98th percentile annual ambient measurement averaged over three consecutive years (Canadian Council of Ministers of the Environment, 2007), thus making the CWS for PM2.5 markedly different from Ontario’s PM2.5 reference level. The 2012 PM2.5 CWS metric concentrations ranged from 13 µg/m3 reported for both Sudbury and Thunder Bay to 25 µg/m3 reported for Hamilton Downtown. The CWS for PM2.5 was not exceeded in 2012 at any of the 21 CWS designated sites. Table A20 of the Appendix provides a complete summary of reported CWS metrics since 2005.

The PM2.5 annual means in Figure 6 display a decreasing trend of 31 per cent for the 10-year period of 2003 to 2012. Similarly, provincial PM2.5  emissions have decreased approximately 25 per cent from 2002 to 2011 as shown in Figure 7. Fine particulate emissions from industrial processes have been reduced approximately 40 per cent during this period. Emissions from the transportation sector decreased 24 per cent with the phase-in of new vehicles/engines having more stringent emission standards over the same period.

Figure 6: Trend of PM2.5 Annual Means Across Ontario (2003-2012)

The fine particulate matter (PM2.5) annual means in Figure 6 display a decreasing trend of 31 per cent for the 10-year period of 2003 to 2012.

Note: The trend is a composite mean based on data from 37 monitoring sites. PM2.5 concentrations as measured by TEOM operated at 30°C with SES.

Figure 6: Ontario PM2.5 Emissions Trend (2002-2011)

The provincial fine particulate matter (PM2.5) emissions  have decreased approximately 25 per cent  from 2002 to 2011 as shown in Figure 7.

Note: Excludes emissions from open and natural sources.

4.0 Other Air Pollutants

Nitrogen Dioxide (NO2)

Nitrogen dioxide is a reddish-brown gas with a pungent odour, which transforms in the atmosphere to form gaseous nitric acid and nitrates. It plays a major role in atmospheric reactions that produce ground-level ozone, a major component of smog. Nitrogen dioxide also reacts in the air and contributes to the formation of PM2.5 (Seinfeld & Pandis, 2006). All combustion in air produces NOX, of which NO2 is a component. Major sources of NOX emissions include the transportation sector, industrial processes and utilities.

Nitrogen dioxide can irritate the lungs and lower their resistance to respiratory infection. People with asthma and bronchitis have increased sensitivity to NO2. Nitrogen dioxide chemically transforms into nitric acid in the atmosphere and, when deposited, contributes to the acidification of lakes and soils in Ontario. Nitric acid can also corrode metals, fade fabrics, degrade rubber, and damage trees and crops.

The Toronto West air monitoring station, located in an area of Toronto influenced by significant vehicular traffic, recorded the highest NO2 annual mean (16.3 ppb) during 2012; whereas Tiverton, a rural site, recorded the lowest NO2 annual mean (2.5 ppb). The highest NO2 means were recorded in large urbanized areas, such as the Greater Toronto Area of southern Ontario. The Toronto West station also recorded the highest one-hour NO2 concentration (70 ppb), and Windsor Downtown recorded the highest 24-hour NO2 concentration (40 ppb). There were no exceedances of the provincial one-hour and 24-hour AAQC for NO2, 100 ppb and 200 ppb, respectively, at any of the monitoring locations in Ontario during 2012.

The NO2 annual mean concentrations across Ontario have decreased 43 per cent from 2003 to 2012, as displayed in Figure 8. The NOX emission trend from 2002 to 2011 indicates a decrease of approximately 39 per cent as shown in Figure 9 (NPRI, 2013). Ontario’s emissions trading regulations on sulphur dioxide and nitrogen oxides (O. Reg. 397/01 and O. Reg. 194/05) have contributed to the reduction in nitrogen oxides emissions in recent years. The NOX emissions from on-road vehicles also decreased due to the phase-in of new vehicles having more stringent emission standards. The implementation of the Ontario Drive Clean program in southern Ontario in 1999 also helped further reduce the NOX emissions from light duty gasoline vehicles.

Figure 8: Trend of NO2 Annual Means Across Ontario (2003-2012)

The nitrogen dioxide annual mean  concentrations across Ontario have decreased  43 per cent from 2003 to 2012.

Note: The trend is a composite mean based on data from 22 monitoring sites.

Figure 9: Ontario NOX Emissions Trend (2002-2011)

The nitrogen oxides emission trend from 2002 to 2011 indicates a decrease of approximately 39 per cent.

Excludes emissions from open and natural sources.

Sulphur Dioxide (SO2)

Sulphur dioxide is a colourless gas that smells like burnt matches. It can also be oxidized in the atmosphere to form sulphuric acid aerosols. In addition, sulphur dioxide is a precursor to sulphates, one of the main components of airborne secondary PM2.5. Electric utilities and smelters are the major sources of SO2 emissions in Ontario, accounting for approximately 64 per cent of the provincial SO2 emissions according to 2011 estimates for point, area and transportation sources (excluding emissions from open and natural sources). Other industrial processes (e.g. petroleum refining, cement and concrete manufacturing) accounted for an additional 27 per cent. The transportation sector and miscellaneous sources accounted for the remaining 9 per cent of all SO2 emissions in the province according to 2011 estimates (NPRI, 2013).

Health effects caused by exposure to high levels of SO2 include breathing problems, respiratory illness, and the exacerbation of respiratory and cardiovascular disease. People with asthma, chronic lung disease or heart disease are the most sensitive to SO2. Sulphur dioxide damages trees and crops. Similar to NO2, SO2 leads to the formation of PM2.5 and is also a precursor to acid rain, which contributes to the acidification of soils, lakes and streams, accelerated corrosion of buildings, and reduced visibility.

Hamilton Downtown recorded the highest SO2 annual mean (4.8 ppb) and 24-hour maximum concentration (29 ppb) during 2012, whereas Sudbury recorded the highest one-hour maximum concentration (142 ppb). There were no exceedances of the provincial one-hour, 24-hour and annual AAQC for SO2, 250 ppb, 100 ppb and 20 ppb, respectively, at any of the monitoring locations in Ontario during 2012.

The SO2 annual mean concentrations from 2003 to 2012 show a decreasing trend of 52 per cent across Ontario in Figure 10. Overall, provincial SO2 emissions have reduced by approximately 55 per cent from 2002 to 2011 as shown in Figure 11 (NPRI, 2013). The reduction of SO2 over the years is the result of various initiatives, which include, but are not limited to,

  • Control orders for Ontario smelters
  • Countdown Acid Rain program and Canada-wide Acid Rain Strategy
  • Ontario emissions trading regulations on sulphur dioxide and nitrogen oxides (O. Reg. 397/01 and O. Reg. 194/05)
  • Phase-out of coal-fired generating stations, with Lakeview Thermal Generating Station shut down in 2005
  • Low sulphur content in transportation fuels.

Figure 10: Trend of SO2 Annual Means Across Ontario (2003-2012)

The sulfur dioxide annual mean concentrations from 2003 to 2012 show a decreasing trend of 52 per cent across Ontario.

Note: Ten-year trend is a composite mean based on 9 sites.

Figure 11: Ontario SO2 Emissions Trend (2002-2011)

The provincial sulfur dioxide emissions have reduced by approximately 55 per cent from 2002 to 2011.

Note: Excludes emissions from open and natural sources.

Carbon Monoxide (CO)

Carbon monoxide is a colourless, odourless, tasteless and, at high concentrations, poisonous gas. This gas can enter the bloodstream and reduce oxygen delivery to the organs and tissues. People with heart disease are particularly sensitive to CO. Exposure to high CO levels is associated with the impairment of vision, work capacity, learning ability and performance of complex tasks. Carbon monoxide is produced primarily by the incomplete combustion of fossil fuels. The 2011 estimates for point, area and transportation sources (excluding emissions from open and natural sources) indicate that the transportation sector accounted for 87 per cent of all CO emissions (NPRI, 2013).

In 2012, the highest one-hour CO maximum, 2.09 parts per million (ppm) and the highest eight-hour maximum (1.21 ppm) were recorded at the Windsor Downtown site. Typically, higher CO concentrations are recorded in urban centres attributable to vehicle emissions.

There were no exceedances of the provincial one-hour and eight-hour AAQC, 30 ppm and 13 ppm, respectively, at any of the monitoring locations in Ontario during 2012.

The annual means of the one-hour and eight-hour CO maximums have decreased 43 per cent and 50 per cent, respectively, across the province from 2003 to 2012. Carbon monoxide emissions have been reduced by approximately 22 per cent from 2002 to 2011 (NPRI, 2013).

5.0 Air Quality Index and Smog Advisories

Ontario Air Quality Index (AQI)

The Air Quality Office of the Environmental Monitoring and Reporting Branch continuously obtains near real-time data for criteria pollutants from 40 AQI sites as displayed in Map A1 of the Appendix. The AQI, based on pollutants that have adverse effects on human health and the environment, includes O3, PM2.5, NO2, SO2, CO and TRS compounds. At the end of each hour, the concentration of each pollutant measured at each site is converted into a number ranging from zero upwards using a common scale or index. The calculated number for each pollutant is a sub-index. At a given air monitoring site, the highest sub-index for any given hour becomes the reporting AQI for that hour. The index is a relative scale, in that the lower the index, the better the air quality. The ministry web site provides index values, corresponding categories, and potential health and environmental effects.

The AQI network provides the public with hourly air quality information (24 hours per day) from across the province. The public can access AQI readings via the ministry’s web site or via the Interactive Voice Response (IVR) system. (To access an English recording, call 1.800.387.7768, or in Toronto, call 416-246-0411. For a French recording, call 1.800.221.8852). The ministry web site and IVR system also provides daily air quality forecasts, based on regional meteorological conditions and current pollution levels in Ontario and bordering U.S. states.

Based on the AQI categories, in 2012, Ontario reported very good to good air quality 92 per cent of the time, and moderate to poor air quality 8 per cent of the time. Table A21 of the Appendix provides the percentage distribution of hourly AQI readings for each of the 40 monitoring sites by AQI category and the number of poor air quality days.

Smog Advisories

Smog advisories are issued to the public in advance when AQI values are expected to be in the poor category due to elevated, widespread and persistent levels of O3 and/ or PM2.5. Generally, smog advisories are issued 24 hours in advance; however, if elevated smog conditions occur suddenly, and weather conditions conducive to elevated smog levels are expected to continue for several hours, a smog advisory is issued effective immediately. Note that a smog advisory is a forecast and does not necessarily mean elevated smog is a certainty since it is based on weather forecasts.

Smog advisories are issued via the ministry’s web site and the ministry’s IVR system (refer to Ontario’s Air Quality Index section above for details), and through email notification as per the Smog Alert network. (To receive a direct email notification of a smog advisory, visit the ministry web site and subscribe to the Smog Alert network).

The ministry issued 12 smog advisories in 2012, which covered 30 days. Table A22 of the Appendix summarizes the number of smog advisories issued for Ontario from 2003.

Glossary

Air Quality Index
real-time information system that provides the public with an indication of air quality in cities, towns and in rural areas across Ontario.
AQI station
continuous monitoring station used to inform the public of general ambient air quality levels over an entire region (not a localized area) on a real-time basis; station reports on criteria pollutant levels that are not unduly influenced by a single emission source, but rather are the result of emissions from multiple sources, including those in neighbouring provinces and states.
Ambient air
outdoor or open air.
Carbon  monoxide
a colourless, odourless, tasteless, and at high concentrations, poisonous gas.
Continuous  pollutants 
pollutants for which a continuous record exists; effectively, pollutants that have hourly data (maximum 8,760 values per year except leap year – e.g. 2004 where maximum values for the year are 8,784).
Continuous  station 
where pollutants are measured on a real-time basis and data determined hourly (for example ozone, sulphur dioxide).
Criterion 
maximum concentration or level (based on potential effects) of pollutant that is desirable or considered acceptable in ambient air.
Exceedance
violation of the air pollutant concentration levels established by environmental protection criteria or other environmental standards.
Fine Particulate Matter
particles smaller than 2.5 microns in aerodynamic diameter, which arise mainly from fuel combustion, condensation of hot vapours and chemically-driven gas-to-particle conversion processes; also referred to as PM2.5 or respirable particles. These are fine enough to penetrate deep into the lungs.
Fossil fuels
natural gas, petroleum, coal and any form of solid, liquid or gaseous fuel derived from organic materials for the purpose of generating heat.
Ground-level ozone
colourless gas formed from chemical reactions between nitrogen oxides and volatile organic compounds (VOCs) in the presence of sunlight near the Earth’s surface.
Micron
a millionth of a metre.
Nitrogen dioxide
a reddish-brown gas with a pungent and irritating odour.
Oxidation 
a chemical reaction where a substance gains an oxygen; for example, in the atmosphere, sulphur dioxide is oxidized by hydroxyl radicals to form sulphate.
Particulate matter
refers to all airborne finely divided solid or liquid material with an aerodynamic diameter smaller than 44 microns.
Percentile value
percentage of the data set that lies below the stated value; if the 70 percentile value is 0.10 ppm, then 70 per cent of the data are equal to or below 0.10 ppm.
Primary  pollutant 
pollutant emitted directly to the atmosphere.
Secondary  pollutant
pollutant formed from other pollutants in the atmosphere.
Smog
a contraction of smoke and fog; colloquial term used for photochemical smog, which includes ozone, and may include fine particulate matter, and other contaminants; tends to be a brownish haze.
Smog advisory
smog advisories are issued to the public when there is a strong likelihood that widespread, elevated and persistent smog levels are expected.
Stratosphere
atmosphere 10 to 40 kilometres above the Earth’s surface.
Stratospheric ozone
ozone formed in the stratosphere from the conversion of oxygen molecules by solar radiation; ozone found there absorbs much ultraviolet radiation and prevents it from reaching the Earth.
Sulphur  dioxide
a colourless gas that smells like burnt matches.
Troposphere
atmospheric layer extending from the surface up to about 10 kilometres above the Earth’s surface.

Acronyms

AAQC
Ambient Air Quality Criteria (Ontario)
AQI
Air Quality Index
CO
carbon monoxide
CWS
Canada-wide Standard
GDAD
Guidance Document on Achievement Determination
IVR
Interactive Voice Response
NO
nitric oxide
NO2
nitrogen dioxide
NOX
nitrogen oxides
O3
ozone
PM2.5
fine particulate matter
SES (TEOM)
Sample Equilibration System
SO2
sulphur dioxide
TEOM
Tapered Element Oscillating Microbalance
TRS
total reduced sulphur
VOCs
volatile organic compounds
kt
kilotonnes
µg/m3
micrograms (of contaminant) per cubic metre (of air) – by weight
ppb
parts (of contaminant) per billion (parts of air) – by volume
ppm
parts (of contaminant) per million (parts of air) – by volume

References

  1. Canadian Council of Ministers of the Environment, 2007. Guidance Document on Achievement Determination: Canada-Wide Standards for Particulate Matter and Ozone (Revised).
  2. NPRI, 2013. National Pollutant Release Inventory (NPRI) Downloadable Datasets. Environment Canada. (accessed February 2013).
  3. Ontario Ministry of the Environment. 2013. Air Quality in Ontario – Report for 2011.
  4. Seinfeld, J.H. and S.N. Pandis. 2006. Atmospheric chemistry and physics: From air pollution to climate change. (2nd ed.) New Jersey: John Wiley & Sons Inc.
  5. Yap, D., Reid, N., De Brou, G. and R. Bloxam. 2005. Transboundary Air Pollution in Ontario. Ontario Ministry of the Environment.

Resources

  1. Brook, J.R., Dann, T. and R.T. Burnett. 1997. The Relationship among TSP, PM10, PM2.5 and Inorganic Constituents of Atmospheric Particulate Matter at Multiple Canadian Locations. Journal of Air and Waste Management Association, Vol 46, pp. 2-18.
  2. Burnett, R.T., Dales, R.E., Krewski, D., Vincent, R., Dann, T., and J.R. Brook. 1995. Associations between Ambient Particulate Sulphate and Admissions to Ontario Hospitals for Cardiac and Respiratory Diseases. American Journal of Epidemiology, Vol 142, pp. 15-22.
  3. Fraser, D., Yap, D., Kiely, P. and D. Mignacca. 1991. Analysis of Persistent Ozone Episodes  in Southern Ontario 1980-1991. Technology Transfer Conference, Toronto, 1991. Proceedings AP14, pp. 222-227.
  4. Geddes, J.A., Murphy, J.G., D.K.Wang. 2009. Long term changes in nitrogen oxides and volatile organic compounds in Toronto and the challenges facing local ozone control. Atmospheric Environment, Vol. 43, pp. 3407-3415.
  5. Itano, Y., Bandow, H., Takenaka, N., Saitoh, Y., Asayama, A., J. Fukuyama. 2007. Impact of NOX reduction on long-term ozone trends in an urban atmosphere. Science of the Total Environment, Vol. 379, pp. 46-55.
  6. Lin, C.C.-Y., Jacob, D.J., Munger, J.W., and A.M. Fiore. 2000. Increasing Background Ozone in Surface Air Over the United States. Geophysical Research Letters, Vol. 27 (21), pp. 3465-3468.
  7. Lioy, P. et al., 1991. Assessing Human Exposure to  Airborne  Pollutants. Environmental Science and Technology, Vol. 25, pp. 1360.
  8. Lipfert, F.W. and T. Hammerstrom. 1992. Temporal Patterns in Air Pollution and Hospital Admissions. Environmental Research, Vol. 59, pp. 374-399.
  9. Lippmann, M. 1991. Health Effects of Tropospheric Ozone. Environmental Science and Technology, Vol. 25, No. 12, pp. 1954-1962.
  10. Logan, J. A., Staehelin, J., Megretskaia, I. A., Cammas, J.-P., Thouret, V., Claude, H., Backer, H. D., Steinbacher, M., Scheel, H.-E., Stubi, R., Frohlich, M., and R. G. Derwent. 2012. Changes in ozone over Europe: Analysis  of  ozone  measurements  from  sondes,  regular  aircraft  (MOZAIC)  and alpine surface sites. Journal of Geophysical Research, 117,  D09301, doi:10.1029/2011JD016952.
  11. Ontario Ministry of the Environment, 2011. Publications. Ontario Ministry of the Environment.
  12. Pengelly, L.D., Silverman, F. and C.H. Goldsmith. 1992. Health Effects of Air Pollution Assessed Using Ontario Health Survey Data. Urban Air Group, McMaster University.
  13. Reid, N., Yap, D., R. Bloxam. 2008. The potential role of background ozone on current and emerging air issues: An overview. Air Quality, Atmosphere & Health, Vol. 1, pp. 19-29.
  14. Rethinking the Ozone Problem in Urban and Regional Air Pollution. National Academy Press, Washington, D.C., 1991.
  15. United States Environmental Protection Agency. 2003. Latest Findings on National Air Quality, 2002 Status and Trends.
  16. United States Environmental Protection Agency. 2003. National Air Quality and Emission Trends, 2003 Special Studies Edition.
  17. United States Environmental Protection Agency. 2004. Particle Pollution Report, Current Understanding of Air Quality and Emissions through 2003.
  18. Vingarzan, R. 2004. A review of surface ozone background levels and trends. Atmospheric Environment, Vol. 38, pp. 3431-42.
  19. Wolff, G.T., Kelley, N.A. and M.A. Ferman. 1982. Source Regions of Summertime Ozone and Haze Episodes in the Eastern U.S. Water, Air and Soil Pollution, 18: pp. 65-81.
  20. Yap, D., Ning, D.T. and W. Dong. 1988. An Assessment of Source Contribution to the Ozone Concentrations in Southern Ontario. Atmospheric Environment, Vol. 22, No. 6, pp. 1161-1168.

Appendix

The Appendix is intended for use in conjunction with the 2012 Annual Air Quality in Ontario report. The Appendix briefly describes the provincial Air Quality Index (AQI) network, quality assurance and quality control procedures, and the Ministry of the Environment and Climate Change’s air quality database. It also includes a series of tables displaying station locations and a listing of the summary statistics including means, maximums, percentile values and the number of exceedances of the Ontario Ambient Air Quality Criteria (AAQC) for each pollutant. In addition, trends for select pollutants are displayed for 10- and 20-year periods.

Monitoring Network Operations

Network Description

In 2012, the Environmental Monitoring and Reporting Branch (EMRB) operated 40 ambient air monitoring sites across Ontario. Monitoring site locations for the AQI network are illustrated in Map A1. The AQI network was comprised of 133 continuous monitoring instruments at 40 sites. These instruments have the capability of recording minute data (approximately 70 million data points per year) that are used to scan and validate the continuous hourly data.

Quality Assurance and Quality Control

Day-to-day maintenance and support of the instruments are administered by EMRB staff. Instrumentation precision is verified by daily automatic internal zero and span checks. Data analysts and station operators review span control charts to confirm instrument precision using a telemetry system. A quarterly quality assurance and quality control (QA/QC) review is performed on the ambient data set in order to highlight anomalies and administer corrective action in a timely manner.

The air monitoring station operators routinely inspect and maintain monitoring equipment and stations with mandatory bi-monthly on- site visits where secondary transfer standards are used to calibrate instrumentation. Station activity is recorded using FieldWorker Inc. software, an electronic documentation solution; this information is transferred directly to the ministry’s database. The instrumentation used throughout the provincial air monitoring network has been standardized to Thermo Electron Corporation analyzers in an effort to streamline parts inventory and leverage common hardware used within each analyzer. The following is a summary of the instrumentation deployed within the network:

  • Ozone – TE49C/I
  • Fine Particulate Matter – TEOM 1400ab/SES
  • Nitrogen Oxides – TE42C/I
  • Carbon Monoxide – TE48C/I
  • Total Reduced Sulphur – TE43C/CDN101
  • Sulphur Dioxide – TE43C/I

EMRB operates a laboratory with gas reference standards that adhere to those of the U.S. National Institute of Standards and Technology (NIST) and the Air Quality Research Division of Environment Canada. The secondary transfer standards used by station operators are referenced and certified to EMRB’s NIST primary standards on a quarterly basis. Primary weighed filter standards from Environment Canada are used to calibrate the TEOM twice a year.

The Ontario ambient air quality monitoring network undergoes constant maintenance to ensure a high standard of quality control.

Continuous real-time data are consistently reviewed, assessed and validated by EMRB staff. Immediate actions are taken to correct any inconsistencies that may affect the validity of the data. These measures ensure ambient air monitoring data are valid, complete, comparable, representative and accurate. As a result, the 2012 ambient air quality monitoring network had greater than 98 per cent valid data from over one million hourly data points.

Continous PM2.5  Monitoring Network Upgrade

The ministry historically relied on the non- continuous Federal Reference Method (FRM) for PM2.5 monitoring, which produces 24-hour averaged measurements on a 3-day or 6-day cycle. The FRM is resource-intensive and requires sample setup and laboratory analysis and can take up to several months to report PM2.5 data. Continuous particulate matter (PM) monitoring is essential for reporting hourly ambient concentrations; however, it comes with technical challenges. The Tapered Element Oscillating Microbalance (TEOM) technology was developed for continuous real-time PM monitoring (Patashnick and Rupprecht, 1991) and received United States Environmental Protection Agency (USEPA) Class III Federal Equivalent Method (FEM) designation in 1990 for PM10 reporting (USEPA, 2011). The Class III FEM is a designation for measuring ambient concentrations of specified air pollutants in accordance with Title 40, Part 53 of the Code of Federal Regulations (40 CFR Part 53).

Ontario was the first province in Canada to report continuous real-time PM2.5 concentrations to the public in 2002 under the AQI program when continuous measurements of PM2.5 became a priority for provincial and federal governments. TEOM was the most innovative method at the time for continuous real-time PM2.5 monitoring, and continues to be used by many jurisdictions across North America. Over the last decade, continuous PM2.5 monitoring technologies have evolved dramatically to address the technical issues associated with cold weather PM2.5 measurements. To ensure consistency and comparability in PM2.5 monitoring and reporting, in 2006, the USEPA published criteria for designating a continuous PM2.5 monitor as Class III FEM (Federal Register, 2006). Manufacturers are required to collocate their PM2.5 monitors with FRM measurements and pass rigorous tests following the USEPA guidelines to receive the Class III FEM PM2.5 designation (Federal Register, 2006). Six continuous PM2.5 monitors received the Class III FEM designation as of October 12, 2011.

After extensive evaluation of four designated Class III FEM PM2.5 monitors, Ontario selected the Thermo Scientific Synchronized Hybrid Ambient Real-time Particulate (SHARP) 5030 to replace the TEOM monitors currently deployed in the AQI network. In 2012, as part of a national initiative funded by Environment Canada, Ontario deployed the SHARP 5030 monitor across Ontario’s ambient air monitoring network. This deployment enables the ministry to learn about the new PM2.5 monitoring method in preparation for the reporting of PM2.5 concentrations as measured by the SHARP 5030 to commence in January 2013. It is anticipated that the SHARP 5030 will report higher PM2.5 concentrations than those reported by TEOM during cold weather due to the improved performance of the SHARP 5030 when compared to measurements with the FRM (Sofowote et al., 2013). Ontario’s upgrade of its PM2.5 monitoring network to the USEPA Class III FEM will standardize monitoring methods and ensure consistency of data quality across Canada.

Data Base

The ambient air quality data used in this report are stored in the ministry’s air quality information system (AQUIS). A statistical pattern test is used to identify data anomalies, such as unusual pollutant concentrations. Each pollutant has a predetermined concentration range based on historical data. Values outside this range are flagged for further investigation.

Data obtained from automated ambient air monitoring instruments that operate continuously to produce an average measurement for every hour for a possible total of 8,760 measurements in a given year. Hourly parameters measured include O3, PM2.5, NO/NO2/NOX, CO, SO2 and TRS compounds. A valid annual mean requires at least 6,570 hourly readings. In addition, the 2nd and 3rd quarters of the year should have 75 per cent valid data for ozone, whereas for PM2.5, each quarter of the year should have 75 per cent valid data (Canadian Council of Ministers of the Environment, 2002).

Network Descriptive Table, Annual Statistics and Trends

The AQI network for 2012 is summarized in Table A1. The table displays the station name, numerical identifier and pollutants measured. The numerical identifier is the station (ID) number, the first digit of which identifies the geographic region in which the station is located.

Table A1 also identifies the type of air monitoring site: ambient, road-side, Canada-wide Standard (CWS), and/or National Air Pollution Surveillance (NAPS). Ambient sites represent the general air quality of an area without any direct influence of local industrial sources. Road-side sites are within approximately 100 m of a major roadway with daily traffic volumes greater than 10,000 vehicles per day.

The 2012 statistical data and 10-year trends for various continuous pollutants are provided in Tables A2-A9, and Tables A10-A18, respectively. To be included in the 10-year trend analysis, a site must have valid annual means for a minimum of 8 years over the 10-year period from 2003-2012. The 20-year trends for ozone, NO2  and SO2  are provided in Figures A1-A26, Figures A27-A40, and Figures A41-A48, respectively. To be included in the 20-year trend analysis, a site must have valid annual means for a minimum of 15 years over the 20-year period from 1993-2012. A linear regression was applied to each of the 20-year trends presented to calculate the per cent change in concentrations over time.

References For Appendix

  1. Canadian Council of Ministers of the Environment, 2002. Guidance Document on Achievement Determination: Canada-Wide Standards for Particulate Matter and Ozone.
  2. Federal Register. 2006. 40 CFR Parts 53 and 58: Revisions to Ambient Air Monitoring Regulations; Final Rule.71 (200), 61236-61328. October 17, 2006.
  3. Patashnick, H. and E.G. Rupprecht. 1991. Continuous PM-10 Measurements Using the tapered Element Oscillating Microbalance. Journal of the Air & Waste Management Association, Vol. 41, pp. 1079-1083.
  4. Sofowote, U., Su, Y., Bitzos, M.M., and Munoz, A. 2013. Improving the Correlations of Ambient  TEOM PM2.5 Data and SHARP 5030  FEM in Ontario: a Multiple Linear Regression Analysis. Journal of the Air & Waste Management Association, in press.
  5. United States Environmental Protection Agency (USEPA). 2011. List of Designated Reference and Equivalent  Methods. Issue Date:  October 12, 2011.

Map A1: Air Quality Index (AQI) Monitoring Sites across Ontario in 2012

A map of Air Quality Index Monitoring Sites across Ontario in 2012.

Table A1: 2012 Ontario Continuous Ambient Air Monitoring Network
ID Station Name Station Location Year Latitude (D:M:S) Longitude (D:M:S) Air Intake (AGL) Type AQI O3 PM2.5 NO2 SO2 CO TRS
12008 Windsor Downtown 467 University Ave. West 1969 42°18'56.8" -83°02'37.2" 8 A/RS/C/N Y T T T T T .
12016 Windsor West College Ave./South Street 1975 42°17'34.4" -83°04'23.3" 4 A/N Y T T T T . T
13001 Chatham 435 Grand Ave. West 2005 42°24'13.3" -82°12'29.9" 15 A/C/N Y T T T . . .
14064 Sarnia Front Street North/CN Tracks, Centennial Park 1978 42°58'56.2" -82°24'18.3" 3 A/N Y T T T T . T
15020 Grand Bend Point Blake Conservation Area 1991 43°19'59.1" -81°44'34.4" 5 A/N Y T T T . . .
15025 London 900 Highbury Ave. North 1995 43°00'24.2" -81°12'23.1" 4 A/C/N Y T T T . . .
16015 Port Stanley 43665 Dexter Line, Elgin Water T. Plant 2002 42°40'19.5" -81°09'46.4" 5 A/N Y T T . . . .
18007 Tiverton 4th Concession/Bruce Road 23 1979 44°18'52.1" -81°32'59.0" 4 A/N Y T T T . . .
21005 Brantford 324 Grand River Ave. 2004 43°08'19.0" -80°17'33.5" 5 A/C/N Y T T T . . .
26060 Kitchener West Ave./Homewood Ave. 1990 43°26'37.8" -80°30'13.7" 5 A/C/N Y T T T . . .
27067 Saint Catharines Argyle Crescent, Pump Station 1987 43°09'36.2" -79°14'05.1" 4 A/C/N Y T T T . . .
28028 Guelph Exhibition Street/Clark Street West 2000 43°33'05.8" -80°15'51.0" 4 A/C/N Y T T T . . .
29000 Hamilton Downtown Elgin St./Kelly St. 1987 43°15'28.0" -79°51'42.0" 4 A/RS/C/N Y T T T T T T
29114 Hamilton Mountain Vickers Rd./East 18th St. 1985 43°13'45.9" -79°51'46.0" 3 A/C/N Y T T T T . .
29118 Hamilton West Main St. West/Hwy 403 1985 43°15'26.8" -79°54'27.9" 3 A/RS Y T T T . . .
31103 Toronto Downtown Bay St./Wellesley St. West 2000 43°39'46.7" -79°23'17.2" 10 A/RS/C/N Y T T T . . .
33003 Toronto East Kennedy Rd./Lawrence Ave. East 1970 43°44'52.5" -79°16'26.6" 4 A/RS/C/N Y T T T . . .
34020 Toronto North Hendon Ave./Yonge St. 1988 43°46'53.8" -79°25'03.8" 5 A/RS/C/N Y T T T . . .
35125 Toronto West 125 Resources Rd. 2003 43°42'34.0" -79°32'36.6" 8 A/RS/C/N Y T T T T T .
44008 Burlington North Shore Blvd. E./Lakeshore Rd. 1979 43°18'54.4" -79°48'09.5" 5 A/C/N Y T T T . . .
44017 Oakville Eighth Line/Glenashton Dr., Halton Reservoir 2003 43°29'12.9" -79°42'08.2" 12 A/C/N Y T T T . . .
45026 Oshawa 2000 Simcoe St. North, Durham College 2005 43°56'45.4" -78°53'41.7" 7 A/RS/C/N Y T T T . . .
46089 Brampton 525 Main St. North, Peel Manor 2000 43°41'55.5" -79°46'51.3" 5 A/C/N Y T T T . . .
46108 Mississauga 3359 Mississauga Rd. North, U of T Mississauga 2007 43°32'49.1" -79°39'31.3" 5 A/C/N Y T T T T . .
47045 Barrie 83 Perry St. 2001 44°22'56.5" -79°42'08.3" 5 A/C/N Y T T T . . .
48006 Newmarket Eagle St. West/McCaffrey Rd. 2001 44°02'39.5" -79°28'59.7" 5 A/N Y T T T . . .
49005 Parry Sound 7 Bay St. 2001 45°20'16.3" -80°02'17.4" 5 A/N Y T T T . . .
49010 Dorset 1026 Bellwood Acres Rd. 1981 45°13'27.4" -78°55'58.6" 3 A/N Y T T . . . .
51001 Ottawa Downtown Rideau St./Wurtemburg St. 1971 45°26'03.6" -75°40'33.6" 4 A/C/N Y T T T T T .
51002 Ottawa Central 960 Carling Ave. 2007 45°22'57.1" -75°42'51.1" 5 A/N Y T T T . . .
51010 Petawawa Petawawa Research Forest Facility 2007 45°59'48.2" -77°26'28.3" 6 A/N Y T T . . . .
52022 Kingston 752 King St. West 2006 44°12'58.5" -76°31'41.9" 13 A/C/N Y T T T . . .
54012 Belleville 2 Sidney St., Water Treatment Plant 2002 44°09'01.9" -77°23'43.8" 10 A/N Y T T T . . .
56010 Morrisburg County Rd. 2, Morrisburg Water Tower 2005 44°53'59.1" -75°11'23.8" 5 A/N Y T T . . . .
56051 Cornwall Bedford St./3rd St. West 1970 45°01'04.7" -74°44'06.8" 4 A/N Y T T T . . .
59006 Peterborough 10 Hospital Dr. 1998 44°18'06.9" -78°20'46.4" 10 A/C/N Y T T T . . .
63203 Thunder Bay 421 James St. South 2004 48°22'45.8" -89°17'24.6" 15 A/RS/C/N Y T T T . . .
71078 Sault Ste. Marie Sault College 2004 46°31'59.5" -84°18'35.7" 8 A/N Y T T T T . T
75010 North Bay Chippewa St. West, Dept. National Defence 1979 46°19'23.5" -79°26'57.4" 4 A/RS/N Y T T T . . .
77219 Sudbury 1222 Ramsey Lake Rd. 2004 46°28'32.5" -80°57'46.6" 3 A/C/N Y T T . T . .
Total 40 40 40 35 10 4 4

Notes:

ID
station identfication number
Year
year station began monitoring
Air intake
height of air intake above ground (m)
Type
type of monitoring site: A = ambient, RS = road-side, C = CWS, N = NAPS
AQI
Air Quality Index site
T
telemetry
O3:
ground-level ozone
PM2.5
fine particulate matter
NO2
nitrogen dioxide
CO
carbon monoxide
SO2
sulphur dioxide
TRS
total reduced sulphur
Table A2: 2012 Ozone (O3) Annual Statistics
Unit: parts per billion (ppb)
O3 1hAAQC: 80 ppb
ID City Station Location Valid h Percentiles (10%) Percentiles (30%) Percentiles (50%) Percentiles (70%) Percentiles (90%) Percentiles (99%) Percentiles (Mean) Maximum (1h) Maximum (24h) No. of Times Above Criterion (1h)
12008 Windsor Downtown 467 University Ave. W. 8741 7 18 26 35 51 76 28.0 128 69 45
12016 Windsor West College Ave./South St. 8666 6 18 26 35 51 75 28.0 128 70 41
13001 Chatham 435 Grand Ave. W. 8710 13 21 28 35 49 74 29.5 104 65 19
14064 Sarnia Front St. N./CN Tracks, Centennial Park 8682 12 22 29 35 49 74 29.7 101 60 41
15020 Grand Bend Point Blake Conservation Area 8761 16 26 32 38 51 82 33.2 124 74 109
15025 London 900 Highbury Ave. N. 8771 10 19 26 33 47 72 27.7 88 62 26
16015 Port Stanley 43665 Dexter Line, Elgin Water T. Plant 8767 17 25 31 38 52 75 33.1 104 68 30
18007 Tiverton 4th Concession/Bruce Rd. 23 8717 18 25 30 36 48 72 32.0 93 66 24
21005 Brantford 324 Grand River Ave. 8773 8 20 28 35 50 72 28.8 88 57 19
26060 Kitchener West Ave./Homewood Ave. 8759 10 20 27 34 47 68 28.0 89 58 9
27067 St. Catharines Argyle Cres., Pump Stn. 8685 9 21 28 35 49 69 28.7 98 63 10
28028 Guelph Exhibition St./Clark St. W. 8685 10 21 28 35 49 71 28.8 94 57 27
29000 Hamilton Downtown Elgin St./Kelly St. 8724 7 18 25 32 45 65 25.7 88 55 7
29114 Hamilton Mountain Vickers Rd./E. 18th St. 8734 12 22 29 36 51 72 30.2 91 70 21
29118 Hamilton West Main St. W./Hwy 403 8771 4 16 24 30 43 64 24.2 85 53 4
31103 Toronto Downtown Bay St./Wellesley St. W. 8763 8 19 25 32 46 69 26.6 90 62 11
33003 Toronto East Kennedy Rd./Lawrence Ave. E. 8680 5 17 23 30 44 69 24.6 89 65 12
34020 Toronto North Hendon Ave./Yonge St. 8769 7 18 25 32 44 70 25.7 92 61 15
35125 Toronto West 125 Resources Rd. 8708 2 12 20 27 42 69 21.5 94 58 23
44008 Burlington North Shore Blvd. E./Lakeshore Rd. 8707 8 18 26 33 46 67 26.7 91 56 5
44017 Oakville Eighth Line/Glenashton Dr., Halton Reservoir 8735 9 20 27 34 47 70 27.7 96 59 11
45026 Oshawa 2000 Simcoe St. N., Durham College 8731 10 20 26 32 43 69 27.0 92 58 9
46089 Brampton 525 Main St. N., Peel Manor 8701 6 18 26 33 46 70 26.6 92 56 15
46108 Mississauga 3359 Mississauga Rd. N., U of T Campus 8747 5 18 25 32 45 67 25.6 81 57 1
47045 Barrie 83 Perry St. 8728 8 19 26 33 43 66 26.3 91 57 16
48006 Newmarket Eagle St. W./Mccaffrey Rd. 8720 12 22 29 35 48 71 29.4 105 64 35
49005 Parry Sound 7 Bay St. 8777 14 24 30 35 46 70 30.1 94 66 16
49010 Dorset 1026 Bellwood Acres Rd. 8776 10 21 28 34 44 65 28.0 82 52 2
51001 Ottawa Downtown Rideau St./Wurtemburg St. 8622 9 19 26 32 42 59 26.0 76 64 0
51002 Ottawa Central 960 Carling Ave. 8664 8 19 26 32 42 58 25.6 76 62 0
51010 Petawawa Petawawa Research Forest Facility 8758 12 22 28 33 43 60 27.7 77 55 0
52022 Kingston 752 King St. W. 8726 17 26 31 37 49 73 32.7 92 67 29
54012 Belleville 2 Sidney St., Water Treatment Plant 8742 12 21 27 33 45 67 28.0 87 59 3
56010 Morrisburg County Rd. 2, Morrisburg Water Tower 8767 11 22 28 34 44 61 28.2 78 62 0
56051 Cornwall Bedford St./3rd St. W. 8592 10 20 27 33 44 59 27.1 76 61 0
59006 Peterborough 10 Hospital Dr. 8707 13 22 28 34 46 70 29.1 90 64 15
63203 Thunder Bay 421 James St. S. 8764 8 19 26 31 39 53 25.0 74 56 0
71078 Sault Ste. Marie Sault College 8765 15 23 28 33 43 66 28.8 82 69 6
75010 North Bay Chippewa St. W., Dept. National Defence 8769 10 20 26 32 42 63 26.1 82 56 1
77219 Sudbury 1222 Ramsey Lake Rd. 8663 15 23 28 33 43 63 28.5 84 63 7
Table A3: 2012 Fine Particulate Matter (PM2.5) Annual Statistics
Unit: micrograms per cubic meter (µg/m3)
PM2.5 24 h Reference Level: 30 µg/m3
ID City Station Location Valid h Percentiles (10%) Percentiles (30%) Percentiles (50%) Percentiles (70%) Percentiles (90%) Percentiles (99%) Percentiles (Mean) Maximum (1h) Maximum (24h) No. of Times Above Criterion (24h)
12008 Windsor Downtown 467 University Ave. W. 8652 1 4 6 9 15 24 7.4 81 22 0
12016 Windsor West College Ave./South St. 8580 1 4 6 10 16 26 7.6 63 22 0
13001 Chatham 435 Grand Ave. W. 8604 0 3 5 8 13 23 6.0 46 20 0
14064 Sarnia Front St. N./CN Tracks, Centennial Park 8583 4 6 9 12 19 30 10.2 93 28 0
15020 Grand Bend Point Blake Conservation Area 8677 0 2 5 8 13 22 5.8 38 20 0
15025 London 900 Highbury Ave. N. 8539 0 3 5 8 14 25 6.5 74 23 0
16015 Port Stanley 43665 Dexter Line, Elgin Water T. Plant 8550 1 3 5 7 12 23 5.9 74 24 0
18007 Tiverton 4th Concession/Bruce Rd. 23 7702 0 2 3 6 11 20 INS 39 19 0
21005 Brantford 324 Grand River Ave. 8711 1 3 5 8 13 25 6.2 101 24 0
26060 Kitchener West Ave./Homewood Ave. 8540 1 3 5 7 13 24 6.0 46 24 0
27067 St. Catharines Argyle Cres., Pump Stn. 8642 1 3 5 8 13 22 6.3 64 19 0
28028 Guelph Exhibition St./Clark St. W. 8661 1 3 5 7 13 23 5.8 48 21 0
29000 Hamilton Downtown Elgin St./Kelly St. 8617 1 4 6 10 18 37 8.3 111 33 3
29114 Hamilton Mountain Vickers Rd./E. 18th St. 8695 1 3 5 8 14 28 6.5 115 31 1
29118 Hamilton West Main St. W./Hwy 403 8612 1 3 6 9 16 32 7.3 76 28 0
31103 Toronto Downtown Bay St./Wellesley St. W. 8627 0 3 5 8 14 25 6.4 45 26 0
33003 Toronto East Kennedy Rd./Lawrence Ave. E. 8622 0 3 5 8 14 24 6.3 70 21 0
34020 Toronto North Hendon Ave./Yonge St. 8683 1 3 6 9 16 27 7.3 43 24 0
35125 Toronto West 125 Resources Rd. 8595 1 3 6 9 15 26 7.1 45 23 0
44008 Burlington North Shore Blvd. E./Lakeshore Rd. 8445 1 3 5 8 14 24 6.4 68 28 0
44017 Oakville Eighth Line/Glenashton Dr., Halton Res. 8639 1 3 5 8 13 23 6.1 42 20 0
45026 Oshawa 2000 Simcoe St. N., Durham College 8412 0 2 4 7 12 21 5.5 38 21 0
46089 Brampton 525 Main St. N., Peel Manor 8421 0 2 4 7 13 24 5.7 57 24 0
46108 Mississauga 3359 Mississauga Rd. N., U of T Campus 8572 1 3 5 7 13 23 6.0 40 21 0
47045 Barrie 83 Perry St. 8658 0 2 4 7 12 23 5.6 79 28 0
48006 Newmarket Eagle St. W./McCaffrey Rd. 8708 0 2 4 7 12 23 5.6 39 22 0
49005 Parry Sound 7 Bay St. 8747 0 2 3 6 11 22 4.8 86 36 1
49010 Dorset 1026 Bellwood Acres Rd. 8707 0 1 3 5 10 19 4.1 36 18 0
51001 Ottawa Downtown Rideau St./Wurtemburg St. 8604 0 2 4 6 11 21 4.8 95 22 0
51002 Ottawa Central 960 Carling Ave. 8680 0 2 4 6 11 20 5.0 32 22 0
51010 Petawawa Petawawa Research Forest Facility 8691 0 1 2 4 9 17 3.6 28 17 0
52022 Kingston 752 King St. W. 8578 1 3 5 8 15 27 6.8 44 24 0
54012 Belleville 2 Sidney St., Water Treatment Plant 8358 0 2 4 7 11 20 5.1 44 19 0
56010 Morrisburg County Rd. 2, Morrisburg Water Tower 8733 1 2 4 6 11 20 5.0 32 20 0
56051 Cornwall Bedford St./3rd St. W. 8641 0 2 4 7 12 25 5.4 57 27 0
59006 Peterborough 10 Hospital Dr. 8615 0 2 4 6 11 20 4.9 50 21 0
63203 Thunder Bay 421 James St. S. 8381 0 2 3 5 9 15 4.1 30 13 0
71078 Sault Ste. Marie Sault College 8213 0 1 3 5 10 21 4.4 86 27 0
75010 North Bay Chippewa St. W., Dept. National Defence 8726 0 2 3 5 10 18 4.1 42 19 0
77219 Sudbury 1222 Ramsey Lake Rd. 8754 0 1 3 5 9 19 4.0 50 33 1

Note:

Measurements taken by Tapered Element Oscillating Microbalance (TEOM) sampler operated at 30 degrees Celsius with a Sample Equilibration System (SES).

INS indicates there was insufficient data in any one quarter to calculate a valid annual mean.

The PM2.5  reference level is 30 µg/m3 for a 24h period based on CWS.

Table A4: 2012 Nitric Oxide (NO) Annual Statistics
Unit: parts per billion (ppb)
ID City Station Location Valid h Percentiles (10%) Percentiles (30%) Percentiles (50%) Percentiles (70%) Percentiles (90%) Percentiles (99%) Percentiles (Mean) Maximum (1h) Maximum (24h)
12008 Windsor Downtown 467 University Ave. W. 8764 0 1 1 3 10 60 4.7 248 92
12016 Windsor West College Ave./South St. 8536 0 0 1 2 8 73 4.6 292 90
13001 Chatham 435 Grand Ave. W. 8678 0 0 1 2 4 16 1.8 95 20
14064 Sarnia Front St. N./CN Tracks, Centennial Park 8689 0 1 1 2 4 20 2.1 89 20
15020 Grand Bend Point Blake Conservation Area 8759 0 0 0 0 1 4 0.3 24 3
15025 London 900 Highbury Ave. N. 8771 1 2 2 4 8 32 4.2 144 36
18007 Tiverton 4th Concession/Bruce Rd. 23 8709 0 0 1 1 1 4 0.7 34 4
21005 Brantford 324 Grand River Ave. 8771 0 0 0 1 2 17 1.1 63 21
26060 Kitchener West Ave./Homewood Ave. 8756 0 0 1 1 3 42 2.1 160 38
27067 St. Catharines Argyle Cres., Pump Stn. 8687 0 0 1 1 4 44 2.5 151 40
28028 Guelph Exhibition St./Clark St. W. 8668 0 1 1 1 3 33 2.2 119 31
29000 Hamilton Downtown Elgin St./Kelly St. 8702 0 1 2 3 10 54 4.6 146 40
29114 Hamilton Mountain Vickers Rd./E. 18th St. 8670 0 0 1 1 4 27 1.9 86 27
29118 Hamilton West Main St. W./Hwy 403 8714 0 1 2 4 15 74 6.3 243 55
31103 Toronto Downtown Bay St./Wellesley St. W. 8701 0 0 1 2 7 31 2.8 126 30
33003 Toronto East Kennedy Rd./Lawrence Ave. E. 8617 0 1 3 6 15 64 6.6 208 75
34020 Toronto North Hendon Ave./Yonge St. 8767 0 1 2 3 12 51 5.0 151 58
35125 Toronto West 125 Resources Rd. 8706 0 2 4 10 29 100 11.3 214 81
44008 Burlington North Shore Blvd. E./Lakeshore Rd. 8202 0 0 1 3 10 58 4.6 204 40
44017 Oakville Eighth Line/Glenashton Dr., Halton Res. 8728 0 0 1 3 7 39 3.4 168 29
45026 Oshawa 2000 Simcoe St. N., Durham College 8686 0 0 1 2 5 19 2.1 90 25
46089 Brampton 525 Main St. N., Peel Manor 8619 0 0 1 2 9 67 4.4 164 47
46108 Mississauga 3359 Mississauga Rd. N., U of T Campus 8619 0 1 1 1 7 57 3.8 142 42
47045 Barrie 83 Perry St. 8768 0 1 1 1 5 44 3.2 239 45
48006 Newmarket Eagle St. W./McCaffrey Rd. 8682 0 0 1 1 3 26 2.0 91 22
49005 Parry Sound 7 Bay St. 8777 0 0 0 0 1 9 0.5 38 6
51001 Ottawa Downtown Rideau St./Wurtemburg St. 8551 0 1 1 2 4 26 2.4 124 30
51002 Ottawa Central 960 Carling Ave. 8664 0 0 0 1 3 42 2.0 94 40
52022 Kingston 752 King St. W. 8721 0 0 0 0 1 4 0.4 46 7
54012 Belleville 2 Sidney St., Water Treatment Plant 8697 0 0 0 1 3 21 1.6 92 21
56051 Cornwall Bedford St./3rd St. W. 8758 0 0 1 1 3 38 2.2 156 38
59006 Peterborough 10 Hospital Dr. 8765 0 1 1 1 3 18 1.8 89 17
63203 Thunder Bay 421 James St. S. 8691 1 2 2 4 12 40 5.1 122 35
71078 Sault Ste. Marie Sault College 8747 0 1 1 1 3 13 1.7 40 7
75010 North Bay Chippewa St. W., Dept. National Defence 8761 1 1 2 2 5 28 2.9 156 20
Table A5: 2012 Nitrogen Dioxide (NO2) Annual Statistics
Unit: parts per billion (ppb)
NO2 1hAAQC: 200 ppb
NO2 24h AAQC: 100 ppb
ID City Station Location Valid h Percentiles (10%) Percentiles (30%) Percentiles (50%) Percentiles (70%) Percentiles (90%) Percentiles (99%) Percentiles (Mean) Maximum (1h) Maximum (24h) No. of Times Above Criterion (1h) No. of Times Above Criterion (24h)
12008 Windsor Downtown 467 University Ave. W. 8764 5 8 11 16 25 40 13.2 58 40 0 0
12016 Windsor West College Ave./South St. 8536 4 6 9 14 23 37 11.4 51 36 0 0
13001 Chatham 435 Grand Ave. W. 8678 1 3 4 7 12 23 5.7 38 24 0 0
14064 Sarnia Front St. N./CN Tracks, Centennial Park 8689 2 4 7 11 18 29 8.6 53 24 0 0
15020 Grand Bend Point Blake Conservation Area 8759 1 2 3 4 8 14 3.6 30 14 0 0
15025 London 900 Highbury Ave. N. 8771 2 3 5 7 12 22 6.3 36 17 0 0
18007 Tiverton 4th Concession/Bruce Rd. 23 8709 0 1 2 3 5 10 2.5 21 10 0 0
21005 Brantford 324 Grand River Ave. 8771 2 3 4 6 12 22 5.4 43 25 0 0
26060 Kitchener West Ave./Homewood Ave. 8756 1 3 5 8 16 32 7.1 60 28 0 0
27067 St. Catharines Argyle Cres., Pump Stn. 8687 3 4 6 9 17 29 8.1 45 22 0 0
28028 Guelph Exhibition St./Clark St. W. 8668 1 3 5 7 15 27 6.5 43 25 0 0
29000 Hamilton Downtown Elgin St./Kelly St. 8702 4 6 9 14 25 37 11.9 51 33 0 0
29114 Hamilton Mountain Vickers Rd./E. 18th St. 8670 3 4 6 10 19 33 8.6 52 33 0 0
29118 Hamilton West Main St. W./Hwy 403 8714 4 7 10 14 24 36 12.1 53 32 0 0
31103 Toronto Downtown Bay St./Wellesley St. W. 8701 5 8 11 16 25 38 13.4 57 36 0 0
33003 Toronto East Kennedy Rd./Lawrence Ave. E. 8617 5 8 12 17 27 40 14.0 52 34 0 0
34020 Toronto North Hendon Ave./Yonge St. 8767 4 7 11 17 27 41 13.4 60 35 0 0
35125 Toronto West 125 Resources Rd. 8706 5 10 14 20 31 44 16.3 70 35 0 0
44008 Burlington North Shore Blvd. E./Lakeshore Rd. 8202 3 6 9 13 23 37 11.0 54 28 0 0
44017 Oakville Eighth Line/Glenashton Dr., Halton Res. 8728 2 4 7 10 20 35 9.1 48 29 0 0
45026 Oshawa 2000 Simcoe St. N., Durham College 8686 2 3 4 6 12 22 5.6 36 23 0 0
46089 Brampton 525 Main St. N., Peel Manor 8619 2 4 7 12 25 40 10.4 55 29 0 0
46108 Mississauga 3359 Mississauga Rd. N., U of T Campus 8619 3 5 7 11 20 32 9.6 45 25 0 0
47045 Barrie 83 Perry St. 8768 3 4 6 9 18 32 8.1 48 26 0 0
48006 Newmarket Eagle St. W./McCaffrey Rd. 8682 2 3 5 8 16 30 7.2 51 32 0 0
49005 Parry Sound 7 Bay St. 8777 1 1 2 3 7 19 3.3 38 13 0 0
51001 Ottawa Downtown Rideau St./Wurtemburg St. 8551 2 3 5 9 17 33 7.8 46 28 0 0
51002 Ottawa Central 960 Carling Ave. 8664 1 2 4 7 16 36 6.6 52 29 0 0
52022 Kingston 752 King St. W. 8721 2 2 3 4 8 19 4.0 33 15 0 0
54012 Belleville 2 Sidney St., Water Treatment Plant 8697 1 2 3 5 10 23 4.7 33 18 0 0
56051 Cornwall Bedford St./3rd St. W. 8758 2 3 4 6 14 31 6.1 51 29 0 0
59006 Peterborough 10 Hospital Dr. 8765 1 1 2 4 8 20 3.7 32 18 0 0
63203 Thunder Bay 421 James St. S. 8691 2 3 5 8 16 29 7.3 46 24 0 0
71078 Sault Ste. Marie Sault College 8747 1 2 3 5 10 21 4.8 42 13 0 0
75010 North Bay Chippewa St. W., Dept. National Defence 8761 1 2 4 6 14 35 6.1 55 23 0 0
Table A6: 2012 Nitrogen Oxides (NOX) Annual Statistics
Unit: parts per billion (ppb)
ID City Station Location Valid h Percentiles (10%) Percentiles (30%) Percentiles (50%) Percentiles (70%) Percentiles (90%) Percentiles (99%) Percentiles (Mean) Maximum (1h) Maximum (24h)
12008 Windsor Downtown 467 University Ave. W. 8764 5 9 13 19 34 96 17.8 290 133
12016 Windsor West College Ave./South St. 8536 4 7 11 16 30 107 16.0 332 126
13001 Chatham 435 Grand Ave. W. 8678 2 4 6 8 15 34 7.5 118 43
14064 Sarnia Front St. N./CN Tracks, Centennial Park 8689 3 5 8 12 22 46 10.7 122 43
15020 Grand Bend Point Blake Conservation Area 8759 1 2 3 5 8 17 3.9 40 17
15025 London 900 Highbury Ave. N. 8771 3 5 8 11 20 51 10.5 165 50
18007 Tiverton 4th Concession/Bruce Rd. 23 8709 1 2 3 4 6 13 3.1 47 14
21005 Brantford 324 Grand River Ave. 8771 2 3 5 7 14 37 6.7 92 46
26060 Kitchener West Ave./Homewood Ave. 8756 2 4 6 9 19 69 9.2 213 66
27067 St. Catharines Argyle Cres., Pump Stn. 8687 3 5 7 10 21 69 10.6 178 60
28028 Guelph Exhibition St./Clark St. W. 8668 2 4 6 9 18 55 8.8 145 50
29000 Hamilton Downtown Elgin St./Kelly St. 8702 5 7 11 18 34 85 16.6 186 67
29114 Hamilton Mountain Vickers Rd./E. 18th St. 8670 3 5 7 11 22 56 10.5 116 55
29118 Hamilton West Main St. W./Hwy 403 8714 5 8 11 18 40 103 18.4 290 78
31103 Toronto Downtown Bay St./Wellesley St. W. 8701 6 9 12 18 31 65 16.2 181 63
33003 Toronto East Kennedy Rd./Lawrence Ave. E. 8617 6 10 15 22 41 98 20.6 248 109
34020 Toronto North Hendon Ave./Yonge St. 8767 4 8 13 21 39 87 18.5 211 89
35125 Toronto West 125 Resources Rd. 8706 6 12 19 30 59 134 27.6 249 114
44008 Burlington North Shore Blvd. E./Lakeshore Rd. 8202 3 6 10 16 32 88 15.6 258 68
44017 Oakville Eighth Line/Glenashton Dr., Halton Res. 8728 3 6 8 13 26 69 12.6 197 58
45026 Oshawa 2000 Simcoe St. N., Durham College 8686 2 4 6 9 16 36 7.8 117 45
46089 Brampton 525 Main St. N., Peel Manor 8619 3 5 8 14 35 100 14.8 212 74
46108 Mississauga 3359 Mississauga Rd. N., U of T Campus 8619 4 6 9 13 27 82 13.4 173 67
47045 Barrie 83 Perry St. 8768 3 5 7 10 23 71 11.3 274 72
48006 Newmarket Eagle St. W./McCaffrey Rd. 8682 3 4 6 9 19 52 9.2 114 53
49005 Parry Sound 7 Bay St. 8777 1 1 2 4 9 26 3.8 54 17
51001 Ottawa Downtown Rideau St./Wurtemburg St. 8551 3 4 7 10 22 55 10.2 153 55
51002 Ottawa Central 960 Carling Ave. 8664 2 3 4 7 19 71 8.7 132 60
52022 Kingston 752 King St. W. 8721 2 3 3 5 9 22 4.6 66 19
54012 Belleville 2 Sidney St., Water Treatment Plant 8697 2 3 4 6 13 43 6.4 114 30
56051 Cornwall Bedford St./3rd St. W. 8758 2 3 5 7 17 64 8.4 204 62
59006 Peterborough 10 Hospital Dr. 8765 1 2 4 5 11 34 5.4 98 35
63203 Thunder Bay 421 James St. S. 8691 4 5 8 13 27 66 12.4 144 53
71078 Sault Ste. Marie Sault College 8747 2 3 4 7 13 32 6.4 71 19
75010 North Bay Chippewa St. W., Dept. National Defence 8761 3 4 5 8 19 58 9.1 206 40
Table A7: 2012 Sulphur Dioxide (SO2) Annual Statistics
Unit: parts per billion (ppb)
SO2 1h AAQC: 250 ppb
SO2 24h AAQC: 100 ppb
SO2 1y AAQC: 100 ppb
ID City Station Location Valid h Percentiles (10%) Percentiles (30%) Percentiles (50%) Percentiles (70%) Percentiles (90%) Percentiles (99%) Percentiles (Mean) Maximum (1h) Maximum (24h) No. of Times Above Criterion (1h) No. of Times Above Criterion (24h) 1y
12008 Windsor Downtown 467 University Ave. W. 8654 0 1 1 2 7 22 2.8 62 18 0 0 0
12016 Windsor West College Ave./South St. 8413 0 0 1 2 8 24 2.8 69 14 0 0 0
14064 Sarnia Front St. N./CN Tracks, Centennial Park 8659 0 0 1 2 11 49 4.1 110 42 0 0 0
29000 Hamilton Downtown Elgin St./Kelly St. 8727 0 1 1 3 15 50 4.8 112 29 0 0 0
29114 Hamilton Mountain Vickers Rd./E. 18th St. 8769 1 1 2 3 8 30 3.7 107 25 0 0 0
35125 Toronto West 125 Resources Rd. 8659 0 0 0 1 2 5 0.6 18 4 0 0 0
46108 Mississauga 3359 Mississauga Rd. N., U of T Campus 8746 0 0 0 1 2 6 0.6 20 3 0 0 0
51001 Ottawa Downtown Rideau St./Wurtemburg St. 8586 0 0 0 0 1 2 0.3 8 2 0 0 0
71078 Sault Ste. Marie Sault College 8758 0 0 0 0 1 13 0.6 56 7 0 0 0
77219 Sudbury 1222 Ramsey Lake Rd. 8767 0 0 0 0 2 27 1.3 142 13 0 0 0
Table A8: 2012 Carbon Monoxide (CO) Annual Statistics
Unit: parts per million (ppm)
CO 1h AAQC: 30 ppm
CO 8h AAQC: 13 ppm
ID City Station Location Valid h Percentiles (10%) Percentiles (30%) Percentiles (50%) Percentiles (70%) Percentiles (90%) Percentiles (99%) Percentiles (Mean) Maximum (1h) Maximum (8h) No. of Times Above Criterion (1h) No. of Times Above Criterion (8h)
12008 Windsor Downtown 467 University Ave. W. 8770 0.17 0.2 0.22 0.26 0.37 0.73 0.26 2.09 1.21 0 0
29000 Hamilton Downtown Elgin St./Kelly St. 8710 0.16 0.19 0.22 0.26 0.40 0.76 0.25 1.71 0.87 0 0
35125 Toronto West 125 Resources Rd. 8711 0.16 0.2 0.23 0.26 0.38 0.7 0.25 1.39 1.20 0 0
51001 Ottawa Downtown Rideau St./Wurtemburg St. 8260 0.14 0.18 0.2 0.24 0.33 0.54 0.23 0.93 0.77 0 0
Table A9: 2012 Total Reduced Sulphur (TRS) Compounds Annual Statistics
Unit: parts per million (ppb)
ID City Station Location Valid h Percentiles (10%) Percentiles (30%) Percentiles (50%) Percentiles (70%) Percentiles (90%) Percentiles (99%) Percentiles (Mean) Maximum (1h) Maximum (24h)
12016 Windsor West College Ave./South St. 8667 0 0 0 1 1 3 0.5 13 2
14064 Sarnia Front St. N./CN Tracks, Centennial Park 8603 0 0 1 1 2 2 0.7 5 2
29000 Hamilton Downtown Elgin St./Kelly St. 8651 0 0 0 0 1 3 0.2 13 4
71078 Sault Ste. Marie Sault College 8677 0 0 0 0 0 1 0.1 4 1
Table A10: 10y Trend for O3
Annual Mean (ppb)
ID City/Town 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 Change Over Time
12008 Windsor Downtown 22.9 20.2 25.3 24.6 27.0 26.9 24.8 28.0 27.2 28.0 up 26%
12016 Windsor West 22.9 22.6 25.6 24.3 25.3 25.9 24.9 26.7 26.4 28.0 up 19%
13001 Chatham INS INS 31.0 28.7 30.9 30.9 28.8 31.9 29.7 29.5 down 1%
14064 Sarnia 24.7 23.8 27.4 26.7 28.6 28.7 26.6 30.7 29.7 29.7 up 22%
15020 Grand Bend 30.7 25.8 32.5 29.7 31.7 31.3 29.6 35.0 32.8 33.2 up 16%
15025 London 26.9 23.6 26.1 25.1 27.2 27.0 25.1 28.2 26.8 27.7 up 9%
16015 Port Stanley 34.9 32.2 34.6 32.4 34.3 34.3 30.9 34.6 32.8 33.1 down 3%
18007 Tiverton 33.2 28.1 31.8 29.0 34.3 32.6 31.4 33.8 32.1 32.0 up 6%
21005 Brantford INS 26.2 27.9 27.0 28.9 28.4 26.5 29.4 28.7 28.8 up 7%
26060 Kitchener 28.1 24.8 28.0 26.6 28.6 28.1 27.0 29.4 27.6 28.0 up 5%
27067 St. Catharines 25.3 23.6 26.3 26.2 28.1 27.5 25.6 28.3 28.0 28.7 up 15%
28028 Guelph 24.4 25.9 28.6 26.8 28.1 27.9 27.3 30.7 28.9 28.8 up 15%
29000 Hamilton Downtown 21.7 20.1 23.3 23.2 24.8 25.1 24.3 26.9 25.4 25.7 up 24%
29114 Hamilton Mountain 28.4 24.6 28.2 27.5 29.2 29.0 27.2 29.7 28.8 30.2 up 10%
29118 Hamilton West 22.0 19.2 21.2 20.9 23.0 23.3 21.8 24.5 24.2 24.2 up 20%
31103 Toronto Downtown 23.6 22.8 24.5 22.6 25.7 26.0 24.6 26.1 25.4 26.6 up 14%
33003 Toronto East 21.8 19.9 22.4 22.0 23.2 21.6 22.1 23.0 23.3 24.6 up 13%
34020 Toronto North 23.6 22.5 24.5 23.3 24.5 22.7 22.1 24.8 23.6 25.7 up 5%
35125 Toronto West 18.7 17.6 20.3 19.0 21.1 20.7 19.5 20.6 20.1 21.5 up 13%
44008 Burlington 22.8 21.0 23.9 23.5 24.6 24.9 24.1 26.6 25.9 26.7 up 21%
44017 Oakville INS 24.6 27.7 26.1 27.5 27.0 25.5 28.0 26.8 27.7 up 6%
45026 Oshawa 24.1 23.3 28.6 25.1 28.0 27.0 25.5 28.0 26.6 27.0 up 10%
46089 Brampton 25.1 25.1 26.8 25.5 26.8 26.6 25.2 27.5 26.1 26.6 up 5%
46108 Mississauga 24.8 20.6 23.1 22.4 23.3 24.6 24.0 25.9 24.1 25.6 up 13%
47045 Barrie 23.2 24.8 26.9 24.1 25.9 26.5 24.3 26.8 25.3 26.3 up 7%
48006 Newmarket 29.6 28.3 30.8 28.8 31.7 29.5 28.6 31.5 27.8 29.4 down 1%
49005 Parry Sound INS 31.1 33.8 30.7 31.8 32.1 29.7 31.3 29.7 30.1 down 7%
49010 Dorset 30.1 28.8 32.3 28.9 29.9 29.3 27.7 28.6 27.0 28.0 down 10%
51001 Ottawa Downtown 24.7 21.7 23.3 23.6 24.7 23.3 23.4 25.7 24.2 26.0 up 9%
54012 Belleville 30.9 28.1 29.4 29.2 32.0 29.8 28.5 30.0 27.9 28.0 down 5%
56010 Morrisburg INS 28.0 27.8 28.0 29.2 27.9 26.1 28.6 27.2 28.2 down 1%
56051 Cornwall 25.9 23.8 27.7 27.5 28.3 26.6 25.5 27.9 26.1 27.1 up 4%
59006 Peterborough 29.7 27.1 31.2 24.9 27.6 28.2 27.7 30.5 27.9 29.1 up 1%
63203 Thunder Bay 26.1 22.0 22.3 23.5 24.2 23.0 24.2 25.7 25.2 25.0 up 7%
71078 Sault Ste. Marie 26.8 27.0 30.2 29.1 29.7 28.9 27.8 28.4 27.8 28.8 up 2%
75010 North Bay 27.0 25.2 28.0 26.7 27.1 27.7 26.1 28.0 26.7 26.1 0%
77219 Sudbury 28.5 27.8 31.0 28.4 28.1 27.9 25.9 28.7 28.7 28.5 down 2%

Notes:

n/a indicates pollutant not monitored

INS indicates there was insufficient data on the 2nd and/or 3rd quarter to calculate a valid annual mean

Station 44017 replaced station 44015 as the Oakville site in 2003

Station 45026 replaced station 45025 as the Oshawa site in 2005.

Station 46108 replaced station 46109 as the Mississauga site in 2009.

Station 46109 replaced station 46110 as the Mississauga site in 2004.

Station 63203 replaced station 63200 as the Thunder Bay site in 2004.

Station 71078 replaced station 71068 as the Sault Ste. Marie site in 2004.

Station 77219 replaced station 77203 as the Sudbury site in 2004.

Table A11: 10y Trend for O3 Summer Means (May - September)
Summer Mean (ppb)
ID City/Town 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 Change Over Time
12008 Windsor Downtown 32.3 26.3 35.6 32.6 36.3 34.1 30.4 34.6 33.8 36.8 up 14%
12016 Windsor West 32.3 29.6 35.8 31.9 33.5 32.1 29.5 31.8 31.9 35.7 up 3%
13001 Chatham n/a INS 39.5 35.5 38.2 36.7 32.6 36.5 34.4 36.6 down 8%
14064 Sarnia 31.8 26.6 34.1 32.0 34.2 33.0 28.6 34.3 32.9 36.6 up 14%
15020 Grand Bend 33.6 29.8 36.3 33.5 34.9 32.4 29.7 37.8 33.9 38.9 up 12%
15025 London 33.9 28.5 33.9 31.2 33.2 31.6 28.4 32.5 30.7 34.4 up 1%
16015 Port Stanley 41.2 35.7 42.3 38.5 40.4 38.8 33.2 38.9 35.5 38.4 down 8%
18007 Tiverton 37.6 29.8 33.3 30.4 38.3 34.0 30.3 33.3 31.7 36.0 down 1%
21005 Brantford INS 28.9 33.5 31.8 33.6 31.0 27.5 31.6 31.1 33.5 up 2%
26060 Kitchener 34.3 29.8 34.3 32.0 34.2 31.0 28.8 31.6 30.2 33.5 down 5%
27067 St. Catharines 31.7 28.3 33.6 32.6 33.9 31.2 27.7 32.0 31.2 35.0 up 4%
28028 Guelph 29.7 29.5 34.0 31.5 33.1 30.4 28.7 32.5 31.3 34.5 up 7%
29000 Hamilton Downtown 28.3 24.9 30.4 29.2 30.8 29.8 28.2 31.6 28.7 32.4 up 13%
29114 Hamilton Mountain 35.0 29.7 36.7 33.7 36.1 33.6 31.0 34.4 32.3 37.4 up 3%
29118 Hamilton West 26.3 22.7 25.7 25.3 26.9 26.7 23.9 27.9 26.2 29.2 up 13%
31103 Toronto Downtown 31.1 28.3 31.9 28.7 33.2 30.9 27.9 31.1 29.5 33.3 up 3%
33003 Toronto East 28.3 24.5 30.6 27.2 28.3 24.9 25.2 26.7 27.4 30.6 up 2%
34020 Toronto North 29.2 26.3 30.2 28.6 29.9 26.4 25.6 28.0 27.5 32.7 up 3%
35125 Toronto West 24.1 21.4 26.5 24.3 25.9 24.8 22.5 24.3 23.6 27.5 up 6%
44008 Burlington 29.0 25.1 30.2 29.2 30.0 28.3 26.7 30.2 29.2 32.5 up 10%
44017 Oakville 35.5 28.6 34.4 31.7 32.8 30.8 28.2 31.5 29.9 34.2 down 5%
45026 Oshawa 27.8 25.9 INS 28.0 31.5 28.3 26.4 29.5 28.5 31.1 up 10%
46089 Brampton 31.2 29.1 31.7 31.3 31.9 31.0 28.5 30.8 29.3 32.7 0%
46108 Mississauga 31.3 24.6 31.6 28.5 28.6 27.3 26.2 29.0 26.7 30.4 down 3%
47045 Barrie 25.7 27.3 30.7 28.1 28.6 30.0 25.0 27.9 26.2 29.7 up 1%
48006 Newmarket 34.7 32.3 36.1 33.7 36.0 32.1 30.9 34.4 30.5 34.2 down 6%
49005 Parry Sound 33.0 33.2 36.9 33.3 33.6 32.2 28.6 30.4 28.7 32.8 down 13%
49010 Dorset 29.5 28.5 33.0 29.2 30.0 27.2 25.0 25.2 23.8 28.3 down 17%
51001 Ottawa Downtown 29.0 23.5 27.2 26.5 28.2 24.9 24.6 26.1 25.1 29.3 0%
54012 Belleville 37.7 33.0 35.6 34.1 37.0 32.3 30.6 34.2 29.9 32.7 down 13%
56010 Morrisburg n/a 29.7 30.6 30.6 31.6 27.8 26.7 29.5 27.1 31.1 down 5%
56051 Cornwall 31.1 26.1 31.8 29.8 31.1 27.6 27.1 29.8 26.7 30.7 down 4%
59006 Peterborough 34.0 30.0 36.5 27.2 30.0 31.6 29.2 32.0 29.8 34.2 down 2%
63203 Thunder Bay 27.3 22.7 23.6 24.7 24.6 21.3 24.2 23.9 24.2 25.3 down 2%
71078 Saulte Ste. Marie 28.0 27.3 32.0 31.4 31.5 28.4 27.5 27.2 26.4 30.3 down 4%
75010 North Bay 29.8 28.4 31.0 29.0 28.5 28.3 26.5 28.4 26.3 28.5 down 9%
77219 Sudbury 32.0 28.7 32.4 30.1 29.5 26.0 25.7 26.3 26.9 29.8 down 14%

Notes:

n/a indicates pollutant not monitored

INS indicates there was insufficient data on the 2nd and/or 3rd quarter to calculate a valid annual mean

Station 44017 replaced station 44015 as the Oakville site in 2003

Station 45026 replaced station 45025 as the Oshawa site in 2005.

Station 46108 replaced station 46109 as the Mississauga site in 2009.

Station 46109 replaced station 46110 as the Mississauga site in 2004.

Station 63203 replaced station 63200 as the Thunder Bay site in 2004.

Station 71078 replaced station 71068 as the Sault Ste. Marie site in 2004.

Station 77219 replaced station 77203 as the Sudbury site in 2004.

Table A12: 10y Trend for O3 Winter Means (January - April, October - December)
Winter Mean (ppb)
ID City/Town 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 Change Over Time
12008 Windsor Downtown 16.4 16.0 16.5 18.8 20.3 21.7 20.8 23.2 22.5 21.7 up 46%
12016 Windsor West 16.1 17.7 18.2 18.8 19.4 21.5 21.6 22.8 22.5 22.3 up 40%
13001 Chatham INS INS 25.1 23.9 25.4 26.8 26.1 28.5 26.7 24.3 up 6%
14064 Sarnia 19.6 22.0 INS 23.0 24.7 25.5 25.2 28.1 27.4 24.7 up 31%
15020 Grand Bend 28.7 22.7 29.8 26.8 29.4 30.5 29.5 33.0 32.1 29.1 up 20%
15025 London 21.8 20.0 20.4 20.7 22.8 23.7 22.8 25.0 24.2 22.9 up 18%
16015 Port Stanley 30.7 29.9 29.2 28.0 30.0 31.0 29.4 31.5 31.0 29.3 up 2%
18007 Tiverton 29.7 INS 30.7 28.2 31.5 31.7 32.3 34.1 32.2 29.2 up 7%
21005 Brantford INS 24.1 23.9 23.6 25.5 26.6 25.8 27.8 27.1 25.4 up 13%
26060 Kitchener 23.7 21.1 23.4 22.7 24.6 26.0 25.9 27.8 25.7 24.0 up 16%
27067 St. Catharines 20.8 20.2 20.9 21.7 24.1 24.9 24.1 25.6 25.8 24.1 up 27%
28028 Guelph 20.8 23.4 24.8 23.4 24.8 26.1 26.4 29.3 27.2 24.8 up 23%
29000 Hamilton Downtown 16.9 16.6 18.2 18.9 20.5 21.7 21.5 23.5 23.1 20.9 up 38%
29114 Hamilton Mountain 23.7 21.1 22.1 23.0 24.2 25.7 24.5 26.3 26.3 25.0 up 19%
29118 Hamilton West 18.9 16.6 17.9 17.8 20.1 20.9 20.4 22.1 22.7 20.6 up 27%
31103 Toronto Downtown 18.2 18.7 19.1 18.2 20.4 22.2 22.4 22.4 22.6 21.8 up 27%
33003 Toronto East 17.2 16.6 17.5 18.2 19.5 19.3 19.9 20.4 20.4 20.3 up 23%
34020 Toronto North 19.7 19.7 20.4 19.4 20.7 20.1 19.5 22.5 20.8 20.7 up 7%
35125 Toronto West 14.6 14.9 15.8 15.1 17.7 17.7 17.4 18.0 17.7 17.2 up 22%
44008 Burlington 18.5 18.1 19.3 19.3 20.7 22.5 22.3 23.9 23.5 22.5 up 33%
44017 Oakville 22.7 21.7 22.8 22.0 23.7 24.4 23.6 25.5 24.7 23.1 up 10%
45026 Oshawa 21.5 21.4 24.1 23.0 25.6 25.7 24.9 26.9 25.2 24.1 up 17%
46089 Brampton 20.8 22.3 23.3 21.4 23.1 23.4 22.8 25.2 23.8 22.2 up 9%
46108 Mississauga 20.2 18.0 17.0 18.0 19.2 22.8 22.5 23.7 22.5 22.2 up 31%
47045 Barrie 21.3 22.9 24.2 21.3 24.0 24.2 23.8 26.0 24.7 23.9 up 13%
48006 Newmarket 26.0 25.4 27.0 25.3 28.6 27.6 27.1 29.4 25.8 26.0 up 4%
49005 Parry Sound INS 29.6 31.6 28.9 30.6 32.0 30.5 31.9 30.4 28.1 down 2%
49010 Dorset 29.0 29.0 31.8 28.6 30.1 30.7 29.6 31.0 29.5 27.7 down 2%
51001 Ottawa Downtown 20.8 20.4 20.7 21.4 22.0 22.2 22.6 25.5 23.6 23.5 up 20%
54012 Belleville 26.1 24.6 25.1 25.8 28.4 28.0 26.9 27.0 26.4 24.6 up 3%
56010 Morrisburg INS 26.6 25.7 26.2 27.5 27.9 25.7 28.0 27.5 26.0 up 2%
56051 Cornwall 22.4 22.2 24.8 25.9 26.3 26.0 24.5 26.5 25.7 24.2 up 10%
59006 Peterborough 26.6 25.0 27.3 23.3 25.9 26.0 26.7 29.5 26.6 25.5 up 5%
63203 Thunder Bay 25.4 21.9 21.7 22.6 23.9 24.3 24.2 27.1 26.1 24.7 up 13%
71078 Sault Ste. Marie 24.7 26.8 28.9 27.5 28.6 29.3 28.4 29.3 28.9 27.6 up 9%
75010 North Bay 25.0 23.0 25.9 25.0 26.2 27.2 25.8 27.7 27.0 24.4 up 8%
77219 Sudbury 25.9 27.2 30.0 27.2 27.2 29.3 26.0 30.5 30.0 27.6 up 7%

Notes:

n/a indicates pollutant not monitored

INS indicates there was insufficient data on the 2nd and/or 3rd quarter to calculate a valid annual mean

Station 44017 replaced station 44015 as the Oakville site in 2003

Station 45026 replaced station 45025 as the Oshawa site in 2005.

Station 46108 replaced station 46109 as the Mississauga site in 2009.

Station 46109 replaced station 46110 as the Mississauga site in 2004.

Station 63203 replaced station 63200 as the Thunder Bay site in 2004.

Station 71078 replaced station 71068 as the Sault Ste. Marie site in 2004.

Station 77219 replaced station 77203 as the Sudbury site in 2004.

Table A13: 10y Trend for PM25
Annual Mean (µg/m3)
ID City/Town 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 Change Over Time
12008 Windsor Downtown 8.5 8.6 10.4 8.2 9.5 8.3 7.2 7.7 7.6 7.4 down 20%
12016 Windsor West 9.6 9.5 10.5 9.2 9.8 8.9 7.4 7.8 7.8 7.6 down 26%
13001 Chatham INS INS 9.1 7.4 7.9 7.3 6.3 6.5 6.6 6.0 down 31%
14064 Sarnia 11.9 12.2 12.9 11.3 12.2 11.4 9.8 10.4 10.5 10.2 down 19%
15020 Grand Bend INS 7.0 7.4 6.5 6.7 6.8 5.8 6.1 6.1 5.8 down 20%
15025 London 7.9 7.8 8.8 6.9 6.5 6.8 5.7 INS 6.2 6.5 down 27%
16015 Port Stanley 8.0 7.5 8.6 7.3 7.2 6.7 5.6 5.9 6.0 5.9 down 32%
18007 Tiverton 6.5 5.8 6.6 5.6 5.6 5.0 4.0 4.5 4.7 INS down 34%
21005 Brantford INS 7.5 8.9 7.6 7.7 6.8 5.8 6.5 6.6 6.2 down 26%
26060 Kitchener 8.1 8.1 9.5 7.7 8.0 7.1 5.8 6.3 6.2 6.0 down 34%
27067 St. Catharines 7.8 7.3 8.6 7.9 8.2 7.4 6.0 6.5 6.3 6.3 down 25%
28028 Guelph 7.3 7.8 8.8 7.0 7.5 6.5 5.6 5.7 5.9 5.8 down 32%
29000 Hamilton Downtown 10.6 8.9 10.0 9.1 8.9 8.3 6.8 7.7 8.1 8.3 down 25%
29114 Hamilton Mountain 9.6 9.3 9.8 8.1 7.8 7.3 6.3 6.2 6.7 6.5 down 40%
29118 Hamilton West INS 8.4 9.6 8.2 8.3 7.6 6.1 6.8 7.1 7.3 down 26%
31103 Toronto Downtown 8.4 7.1 8.5 7.3 7.3 6.6 5.6 6.0 6.2 6.4 down 28%
33003 Toronto East 8.8 7.4 8.4 7.6 7.8 6.7 5.9 6.7 6.2 6.3 down 30%
34020 Toronto North 8.3 7.7 9.4 7.6 7.8 7.3 5.9 6.2 7.7 7.3 down 20%
35125 Toronto West 9.8 9.8 10.0 8.2 8.4 7.5 6.1 6.5 6.9 7.1 down 38%
44008 Burlington 8.6 7.9 9.1 7.6 7.3 6.9 5.9 6.2 6.2 6.4 down 33%
44017 Oakville INS 8.1 8.9 7.4 7.6 6.7 5.3 5.7 6.4 6.1 down 34%
45026 Oshawa INS INS 8.1 6.8 6.8 6.3 5.2 5.6 5.5 5.5 down 33%
46089 Brampton 8.2 7.7 8.9 7.2 7.4 6.8 5.6 5.8 6.0 5.7 down 36%
46108 Mississauga 7.9 8.0 9.2 7.6 7.2 7.1 5.8 6.1 6.0 6.0 down 33%
47045 Barrie 7.5 6.9 8.1 6.7 6.9 6.1 5.2 5.4 5.7 5.6 down 31%
48006 Newmarket 7.3 6.4 7.7 6.4 6.6 6.0 5.1 5.6 5.5 5.6 down 28%
49005 Parry Sound INS 5.3 6.1 5.3 5.5 4.7 3.9 4.4 4.7 4.8 down 23%
49010 Dorset 5.9 4.7 5.8 4.5 5.0 4.5 3.6 4.0 4.1 4.1 down 32%
51001 Ottawa Downtown 7.2 6.5 7.7 6.1 6.0 5.3 4.6 4.5 4.9 4.8 down 41%
54012 Belleville 6.9 6.4 7.0 6.2 6.2 6.1 4.9 INS 4.8 5.1 down 31%
56010 Morrisburg INS 6.2 7.0 6.8 6.2 5.7 5.0 5.3 5.2 5.0 down 29%
56051 Cornwall INS 6.8 7.6 6.5 6.4 6.1 5.4 5.7 5.7 5.4 down 26%
59006 Peterborough 6.7 5.9 7.5 6.3 6.4 6.0 4.9 5.1 5.5 4.9 down 28%
63203 Thunder Bay INS 4.2 4.4 4.8 4.4 4.2 3.8 4.1 4.8 4.1 down 4%
71078 Sault Ste. Marie INS 4.5 5.4 5.2 5.3 4.4 4.0 4.1 4.4 4.4 down 18%
75010 North Bay 5.5 4.5 5.6 4.9 5.0 4.6 3.8 3.8 4.2 4.1 down 28%
77219 Sudbury INS INS 5.1 4.6 4.9 4.1 3.4 3.6 4.0 4.0 down 32%

Notes:

Measurements taken by Tapered Element Oscillating Microbalance (TEOM) sampler operated at 30°C with a Sample Equilibration System (SES).

INS indicates there was insufficient data on the 2nd and/or 3rd quarter to calculate a valid annual mean

Station 44017 replaced station 44015 as the Oakville site in 2003

Station 45026 replaced station 45025 as the Oshawa site in 2005.

Station 46108 replaced station 46109 as the Mississauga site in 2009.

Station 46109 replaced station 46110 as the Mississauga site in 2004.

Station 63203 replaced station 63200 as the Thunder Bay site in 2004.

Station 71078 replaced station 71068 as the Sault Ste. Marie site in 2004.

Station 77219 replaced station 77203 as the Sudbury site in 2004.

Table A14: 10y Trend for NO
Annual Mean (ppb)
ID City/Town 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 Change Over Time
12008 Windsor Downtown INS 10.5 7.8 7.2 6.4 5.9 5.6 4.7 4.5 4.7 down 58%
12016 Windsor West INS 11.3 8.3 7.2 6.5 5.1 5.4 6.1 3.8 4.6 down 62%
13001 Chatham INS INS 2.5 2.6 2.4 3.1 3.5 2.6 1.9 1.8 down 22%
14064 Sarnia 5.0 3.7 3.8 3.7 3.2 3.2 2.8 2.2 3.1 2.1 down 51%
15025 London INS 6.0 5.5 4.4 3.6 3.1 2.8 2.9 3.3 4.2 down 45%
21005 Brantford INS 2.8 3.8 2.5 1.8 1.3 1.7 1.3 1.2 1.1 down 74%
26060 Kitchener INS 4.9 4.4 3.5 2.7 2.5 2.1 2.5 2.0 2.1 down 64%
29000 Hamilton Downtown 11.7 9.6 9.9 8.0 7.7 6.5 5.8 5.0 4.8 4.6 down 64%
31103 Toronto Downtown 8.7 7.6 7.2 7.0 5.9 5.0 5.1 4.1 3.4 2.8 down 67%
33003 Toronto East 17.0 16.0 14.4 12.5 10.8 9.2 7.8 7.8 7.6 6.6 down 67%
34020 Toronto North 12.4 10.5 10.8 10.0 8.3 7.7 7.1 5.7 6.2 5.0 down 60%
35125 Toronto West 30.2 26.6 26.1 20.1 17.5 16.2 13.5 13.4 12.4 11.3 down 68%
44008 Burlington 14.0 11.1 12.3 9.8 8.8 6.5 5.9 5.0 4.6 4.6 down 75%
44017 Oakville INS 5.3 5.2 4.3 3.9 4.0 3.5 3.6 2.7 3.4 down 43%
45026 Oshawa 9.33 8.22 INS 3.8 3.2 3.2 3.0 2.3 2.3 2.1 down 89%
46089 Brampton 10.4 8.7 8.9 9.1 6.0 5.8 6.5 3.7 4.6 4.4 down 63%
47045 Barrie 9.3 7.3 7.1 8.0 5.5 5.5 5.1 4.3 3.8 3.2 down 64%
48006 Newmarket 4.0 3.1 3.5 3.0 2.2 2.6 3.2 2.3 2.2 2.0 down 45%
51001 Ottawa Downtown 5.8 3.2 3.3 3.0 3.4 2.7 2.4 1.6 1.8 2.4 down 63%
54012 Belleville 6.1 5.6 4.5 3.0 3.2 3.0 1.9 2.3 2.3 1.6 down 78%
59006 Peterborough 3.4 n/a n/a 2.5 2.3 3.0 1.9 1.7 2.2 1.8 down 47%
75010 North Bay 6.4 8.8 3.7 4.4 3.5 3.8 4.2 3.4 4.0 2.9 down 57%

Notes:

n/a indicates pollutant not monitored

INS indicates there was insufficient data on the 2nd and/or 3rd quarter to calculate a valid annual mean

Station 44017 replaced station 44015 as the Oakville site in 2003

Station 45026 replaced station 45025 as the Oshawa site in 2005.

Table A15: 10y Trend for NO2
Annual Mean (ppb)
ID City/Town 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 Change Over Time
12008 Windsor Downtown INS 18.3 16.9 17.2 17.2 15.2 14.4 15.6 14.5 13.2 down 25%
12016 Windsor West INS 17.6 17.1 15.7 16.1 16.2 13.2 14.5 12.9 11.4 down 32%
13001 Chatham INS INS 11.0 9.5 8.6 7.0 7.5 6.4 6.6 5.7 down 47%
14064 Sarnia 13.1 11.7 12.7 11.0 11.3 10.8 8.2 8.0 8.6 8.6 down 40%
15025 London INS 13.7 14.1 12.3 11.7 10.8 9.0 8.8 8.3 6.3 down 53%
21005 Brantford INS 8.6 10.1 8.8 7.7 6.9 7.3 5.8 6.1 5.4 down 43%
26060 Kitchener INS 13.1 12.9 10.8 9.7 9.0 8.6 7.7 7.7 7.1 down 49%
29000 Hamilton Downtown 21.3 16.8 19.3 17.0 17.0 14.7 13.6 12.7 13.5 11.9 down 42%
31103 Toronto Downtown 23.2 20.1 20.7 19.2 18.2 17.0 16.5 16.1 14.9 13.4 down 38%
33003 Toronto East 21.3 19.8 20.1 17.4 17.2 16.5 14.9 14.8 15.2 14.0 down 35%
34020 Toronto North 20.4 17.3 19.2 17.4 16.7 16.5 15.8 14.3 15.4 13.4 down 29%
35125 Toronto West 26.2 24.8 26.6 22.3 22.1 20.8 19.0 20.1 19.1 16.3 down 36%
44008 Burlington 17.3 15.3 17.2 16.2 16.0 13.6 12.5 12.2 11.8 11.0 down 37%
44017 Oakville INS 13.5 14.5 12.5 13.0 12.0 11.1 9.2 10.3 9.1 down 36%
45026 Oshawa 16.2 14.2 INS 8.9 8.1 8.5 7.4 7.2 7.0 5.6 down 67%
46089 Brampton 17.6 16.2 16.9 15.2 13.9 13.1 13.3 10.7 11.3 10.4 down 42%
47045 Barrie 14.8 13.3 13.8 12.6 11.5 10.8 9.9 8.7 8.6 8.1 down 47%
48006 Newmarket 10.2 9.9 8.5 9.0 8.3 8.0 7.8 7.2 8.1 7.2 down 28%
51001 Ottawa Downtown 13.7 11.1 9.8 8.6 8.7 11.4 8.6 7.4 7.9 7.8 down 39%
54012 Belleville 10.5 9.4 8.2 4.5 6.4 7.3 6.0 5.5 6.3 4.7 down 49%
59006 Peterborough 8.3 n/a n/a 6.3 6.4 7.0 5.6 5.0 4.3 3.7 down 52%
75010 North Bay 10.1 9.2 6.8 7.7 7.4 7.5 8.2 7.6 7.4 6.1 down 25%

Notes:

n/a indicates pollutant not monitored

INS indicates there was insufficient data on the 2nd and/or 3rd quarter to calculate a valid annual mean

Station 44017 replaced station 44015 as the Oakville site in 2003

Station 45026 replaced station 45025 as the Oshawa site in 2005.

Table A16: 10y Trend for NOX
Annual Mean (ppb)
ID City/Town 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 Change Over Time
12008 Windsor Downtown INS 29.3 24.9 24.4 23.6 21.1 20.0 20.2 18.9 17.8 down 37%
12016 Windsor West INS 29.1 25.6 22.8 22.6 21.3 18.6 20.6 16.7 16.0 down 43%
13001 Chatham INS INS 13.5 12.1 11.0 10.1 10.9 9.0 8.4 7.5 down 42%
14064 Sarnia 18.1 15.7 16.8 14.7 14.5 13.9 11.0 10.2 11.7 10.7 down 44%
15025 London INS 19.4 19.4 16.7 15.3 13.9 11.9 11.7 11.6 10.5 down 50%
21005 Brantford INS 11.6 13.7 11.3 9.5 8.2 9.1 7.2 7.3 6.7 down 50%
26060 Kitchener INS 18.2 17.4 14.3 12.4 11.5 10.8 10.3 9.6 9.2 down 53%
29000 Hamilton Downtown 33.3 27.7 30.1 24.9 24.7 21.2 19.5 17.8 18.3 16.6 down 52%
31103 Toronto Downtown 32.2 28.1 28.2 26.1 24.2 22.1 21.6 20.3 18.4 16.2 down 47%
33003 Toronto East 37.9 36.3 34.7 29.9 28.0 25.7 22.7 22.6 22.8 20.6 down 49%
34020 Toronto North 33.1 28.3 30.4 27.5 25.0 24.3 22.8 20.0 21.5 18.5 down 42%
35125 Toronto West 56.9 51.2 52.4 42.4 39.6 37.0 32.5 33.5 31.5 27.6 down 53%
44008 Burlington 31.0 26.1 29.3 26.0 24.8 20.0 18.4 17.2 16.4 15.6 down 53%
44017 Oakville INS 18.3 19.5 16.7 16.9 16.1 14.6 12.8 13.0 12.6 down 37%
45026 Oshawa 25.5 22.5 INS 12.7 11.3 11.7 10.4 9.5 9.2 7.8 down 75%
46089 Brampton 28.1 25.0 25.9 24.2 19.9 18.9 19.9 14.4 15.9 14.8 down 50%
47045 Barrie 24.2 20.8 21.0 20.6 17.0 16.3 15.1 13.1 12.4 11.3 down 54%
48006 Newmarket 14.1 13.0 12.2 11.8 10.4 10.4 11.0 9.5 10.3 9.2 down 33%
51001 Ottawa Downtown 20.1 14.7 13.7 11.5 12.0 14.0 11.0 9.0 9.7 10.2 down 48%
54012 Belleville 15.8 14.4 12.6 7.5 9.6 10.2 7.9 7.8 8.7 6.4 down 57%
59006 Peterborough 11.7 n/a n/a 8.8 8.6 10.0 7.5 6.7 6.6 5.4 down 51%
75010 North Bay 16.4 19.0 11.2 12.1 10.9 11.3 12.4 11.0 11.5 9.1 down 41%

Notes:

n/a indicates pollutant not monitored

INS indicates there was insufficient data on the 2nd and/or 3rd quarter to calculate a valid annual mean

Station 44017 replaced station 44015 as the Oakville site in 2003

Station 45026 replaced station 45025 as the Oshawa site in 2005.

Table A17: 10y Trend for CO
1-hour Maximum (ppm)
CO 1-hour AAQC is 30 ppm
ID City/Town 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 Change Over Time
12008 Windsor Downtown 4.3 2.3 1.3 2.9 5.0 1.3 1.4 2.5 3.8 2.1 down 23%
29000 Hamilton Downtown 3.1 4.0 2.6 2.8 6.0 3.3 5.0 2.2 1.8 1.7 down 35%
35125 Toronto West 3.4 2.9 2.7 3.0 1.4 1.7 1.6 1.8 1.4 1.4 down 65%
51001 Ottawa Downtown 2.2 2.2 2.0 1.4 1.5 1.3 1.4 1.5 1.5 0.9 down 50%
Table A18: 10y Trend for SO2
Annual Mean (ppb)
SO2 1-year AAQC is 20 ppb
ID City/Town 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 Change Over Time
12008 Windsor Downtown 5.9 4.8 4.9 5.0 5.5 4.5 3.5 3.5 3.5 2.8 down 47%
12016 Windsor West 6.4 4.6 5.1 4.9 5.2 4.7 3.6 3.2 3.4 2.8 down 50%
14064 Sarnia 7.1 8.2 7.8 8.3 8.0 7.7 4.5 3.9 5.3 4.1 down 49%
29000 Hamilton Downtown 5.0 4.0 5.3 4.8 4.2 4.3 3.3 3.3 5.2 4.8 down 9%
29114 Hamilton Mountain 5.3 n/a n/a 3.3 3.5 3.0 3.0 2.9 4.1 3.7 down 28%
35125 Toronto West 2.9 2.7 2.3 2.0 1.5 1.4 1.2 0.9 1.5 0.6 down 76%
51001 Ottawa Downtown INS 1.0 1.5 1.1 0.9 1.0 0.9 0.2 0.4 0.3 down 81%
71078 Sault Ste. Marie 2.0 0.9 1.5 1.4 1.8 1.2 0.6 0.7 0.8 0.6 down 64%
77219 Sudbury 2.0 INS 2.8 2.4 2.3 2.0 1.1 1.3 1.5 1.3 down 51%

Notes:

n/a indicates pollutant not monitored

INS indicates there was insufficient data on the 2nd and/or 3rd quarter to calculate a valid annual mean

Station 71078 replaced station 71068 as the Sault Ste. Marie site in 2004.

Station 77219 replaced station 77203 as the Sudbury site in 2004.

Table A19: Ozone CWS Metric for Designated Sites Across Ontario
Unit: (ppb)
City/Town 2003 - 2005 2004 - 2006 2005 - 2007 2006 - 2008 2007 - 2009 2008 - 2010 2009 - 2011 2010 - 2012 Change Over Time
Windsor Downtown 82* 81* 89* 85* 81* 74* 75* 79* down 10%
Chatham n/a 86* 86* 80* 78* 73* 72* 75* down 17%
London 74* 70* 73* 72* 69* 67* 65 71* down 8%
Brantford n/r n/r n/r n/r n/r n/r 72* 74*
Kitchener 79* 74* 77* 74* 71* 68* 66* 69* down 15%
Guelph 79* 77* 79* 75* 73* 70* 69* 72* down 12%
St. Catharines 81* 75* 81* 76* 73* 67* 67* 70* down 17%
Hamilton Downtown 77* 72* 76* 74* 71* 69* 67* 68* down 12%
Hamilton Mountain 82* 76* 80* 76* 74* 71* 70* 72* down 13%
Burlington 75* 72* 76* 74* 71* 68* 66* 69* down 11%
Oakville 81* 74* 80* 77* 75* 71* 69* 71* down 13%
Mississauga 80* 75* 80* 77* 66* 66* 65 68* down 19%
Brampton 80* 75* 79* 76* 74* 69* 68* 70* down 14%
Toronto 81* 75* 80* 78* 76* 74* 71* 73* down 10%
Oshawa n/a 77* 80* 76* 74* 70* 68* 71* down 13%
Barrie 72* 69* 72* 71* 70* 67* 62 67* down 10%
Peterborough 81* 72* 73* 71* 73* 73* 71* 73* down 6%
Kingston 77* 77* 89* 85* 81* 77* 74* 76* down 6%
Ottawa Downtown 69* 67* 71* 68* 65 61 58 60 down 17%
Sudbury 76* 74* 77* 71* 69* 66* 65 66*  down 16%
Thunder Bay 58 57 57 55 53 54 54 56 down 6%

Notes:

The CWS for ozone is 65 ppb, which is based on eight-hour running average time and the 4th highest annual ambient measurement averaged over three consecutive years.

CWS metrics are calculated as per the GDAD.

Toronto reporting is based on Toronto Downtown, Toronto North, Toronto East and Toronto West sites.

* indicates an exceedance of the CWS.

n/a indicates data are not sufficient to calculate metrics.

n/r indicates site not designated for CWS reporting. Brantford was added as a CWS designated site in 2009-2011.

A linear regression is applied to derive per cent change over time.

Table A20: PM2.5 CWS Metric for Designated Sites Across Ontario
Unit: micrograms per cubic metre (µg/m3)
City/Town 2003 - 2005 2004 - 2006 2005 - 2007 2006 - 2008 2007 - 2009 2008 - 2010 2009 - 2011 2010 - 2012 Change Over Time
Windsor Downtown 31* 29 29 25 23 21 21 21 down 37%
Chatham n/a 28 28 25 23 20 19 19 down 38%
London 30 28 26 23 22 20 17 17 down 46%
Brantford n/r n/r n/r n/r n/r n/r 20 20
Kitchener 34* 30 29 25 22 19 18 19 down 50%
Guelph 34* 30 28 24 21 19 18 18 down 52%
St. Catharines 29 30 31* 27 23 20 19 19 down 43%
Hamilton Downtown 34* 32* 32* 29 25 23 22 25 down 36%
Hamilton Mountain 32* 31* 29 26 23 21 19 20 down 44%
Burlington 30 29 28 25 22 21 19 20 down 40%
Oakville 34* 30 28 24 21 19 18 18 down 52%
Mississauga 34* 32* 29 27 19 19 17 18 down 56%
Brampton 31* 29 28 24 22 19 17 18 down 48%
Toronto 33* 31* 30 25 22 20 19 20 down 47%
Oshawa n/a 29 29 25 21 19 18 18 down 45%
Barrie 30 29 28 24 21 18 17 18 down 48%
Peterborough 28 29 28 23 20 17 17 18 down 47%
Kingston n/a n/a 30 28 24 23 22 24 down 24%
Ottawa Downtown 30 26 25 20 17 15 14 15 down 58%
Sudbury n/a 20 21 18 16 13 12 13 down 45%
Thunder Bay n/a n/a 16 15 14 13 14 13 down 17%

Notes:

The CWS for PM2.5 is 30 µg/m3, 24-hour average time, based on the 98th percentile annual ambient measurement averaged over three consecutive years.

CWS metrics are calculated as per the GDAD.

Toronto reporting is based on Toronto Downtown, Toronto North, Toronto East and Toronto West sites.

* indicates an exceedance of the CWS.

n/a indicates data are not sufficient to calculate metrics.

n/r indicates site not designated for CWS reporting. Brantford was added as a CWS designated site in 2009-2011.

A linear regression is applied to derive per cent change over time.

Table A21: 2012 Air Quality Summary
City/Town No. of valid Hours % of Valid Hours AQI in Range (Very Good
0-15)
% of Valid Hours AQI in Range (Good
16-31)
% of Valid Hours AQI in Range (Moderate
32-49)
% of Valid Hours AQI in Range (Poor
50-99)
% of Valid Hours AQI in Range (Very Poor
100+)
No. of Days At Least 1 Hour > 49
Windsor Downtown 8781 35.8 53.1 10.5 0.5 0 14
Windsor West 8698 35.4 52.9 11.2 0.5 0 13
Chatham 8715 34.3 56.1 9.4 0.2 0 6
Sarnia 8753 21.6 66.8 11.1 0.6 0 16
Grand Bend 8769 22.1 67.0 9.7 1.2 0 22
London 8775 36.5 54.7 8.4 0.3 0 11
Port Stanley 8781 23.7 64.4 11.6 0.3 0 10
Tiverton 8726 22.2 69.2 8.3 0.3 0 11
Brantford 8777 31.6 57.8 10.3 0.3 0 8
Kitchener 8765 34.0 57.8 8.0 0.1 0 3
St. Catharines 8693 32.0 58.7 9.2 0.1 0 3
Guelph 8712 31.7 59.0 9.0 0.3 0 8
Hamilton Downtown 8772 36.5 52.7 10.4 0.4 0 9
Hamilton Mountain 8772 28.2 60.1 11.4 0.3 0 7
Hamilton West 8776 39.5 52.6 7.8 0.1 0 3
Toronto Downtown 8765 40.1 52.1 7.6 0.1 0 4
Toronto East 8778 45.5 47.8 6.7 0.1 0 4
Toronto North 8776 36.7 56.1 7.1 0.2 0 5
Toronto West 8771 50.9 41.8 7.0 0.3 0 9
Burlington 8767 37.7 54.5 7.7 0.1 0 2
Oakville 8745 36.1 55.4 8.3 0.1 0 4
Oshawa 8764 36.9 57.8 5.2 0.1 0 5
Brampton 8717 36.9 55.2 7.8 0.2 0 5
Mississauga 8755 39.7 53.5 6.8 <0.1 0 1
Barrie 8781 37.3 57.4 5.0 0.3 0 7
Newmarket 8782 31.8 60.0 7.9 0.4 0 11
Parry Sound 8782 27.1 66.2 6.4 0.3 0 6
Dorset 8780 34.1 60.6 5.4 <0.1 0 2
Ottawa Downtown 8682 38.9 57.1 4.0 <0.1 0 0
Ottawa Central 8730 39.2 57.1 3.7 0 0 0
Petawawa 8763 33.9 62.1 4.0 0 0 0
Kingston 8733 20.3 70.0 9.3 0.3 0 8
Belleville 8749 34.9 59.0 6.0 <0.1 0 2
Morrisburg 8774 31.9 62.9 5.2 0 0 0
Cornwall 8775 35.4 59.6 5.0 0 0 0
Peterborough 8773 32.1 61.1 6.6 0.2 0 5
Thunder Bay 8775 40.6 57.8 1.6 0 0 0
Sault Ste. Marie 8772 31.2 63.9 4.7 0.2 0 5
North Bay 8776 38.8 57.7 3.4 <0.1 0 1
Sudbury 8782 32.5 63.3 4.1 0.1 0 3
Table A22: Summary of Smog Advisories (2003 - 2012)
Air Quality Forecast Region 2003 Adv. 2003 Days 2004 Adv. 2004 Days 2005 Adv. 2005 Days 2006 Adv. 2006 Days 2007 Adv. 2007 Days 2008 Adv. 2008 Days 2009 Adv. 2009 Days 2010 Adv. 2010 Days 2011 Adv. 2011 Days 2012 Adv. 2012 Days
Algonquin 2 4 3 6 5 16 1 3 1 3 0 0 1 1 0 0 0 0 1 3
Bancroft-Bon Echo 5 12 6 12 7 21 1 3 4 13 2 3 2 4 1 5 0 0 2 5
Barrie-Orillia-Midland 4 11 5 12 13 39 5 11 8 21 3 7 2 4 1 4 1 1 7 15
Belleville-Quinte-Northumberland 5 12 5 10 13 42 5 12 9 24 4 8 2 4 2 8 1 1 6 13
Brockville-Leeds and Grenville 4 9 5 10 7 24 2 5 3 5 2 4 2 4 1 2 0 0 2 4
Burk’s Falls Bayfield Inlet 4 10 5 11 8 24 2 4 1 3 0 0 1 1 0 0 0 0 2 4
City of Hamilton 6 15 6 15 13 45 5 11 10 31 6 13 2 4 2 8 2 2 7 18
City of Ottawa 3 5 1 1 7 25 2 5 2 4 1 1 2 4 1 2 0 0 1 2
City of Toronto 5 12 6 14 14 48 5 11 11 29 6 13 2 4 2 8 1 1 8 16
Cornwall-Morrisburg 3 5 1 1 7 25 2 5 3 5 2 4 2 4 1 2 0 0 1 2
Dufferin-Innisfil 5 12 5 13 13 44 5 11 9 27 3 7 2 4 1 5 1 1 7 15
Dunnville-Caledonia-Haldimand 5 14 6 16 13 45 5 11 12 31 4 11 2 4 2 8 1 1 6 16
Elgin 5 15 6 16 12 45 4 13 13 37 6 15 2 4 2 10 2 4 7 18
Elliot Lake-Ranger Lake 1 5 0 0 4 12 1 3 1 3 0 0 0 0 0 0 0 0 2 4
Greater Sudbury and Vicinity 1 4 0 0 7 20 2 4 1 3 0 0 1 1 0 0 0 0 2 4
Grey-Bruce 4 11 4 10 10 32 4 10 9 22 1 2 2 4 2 8 1 1 6 14
Haliburton 4 10 6 12 10 30 4 10 6 17 1 2 2 4 1 4 0 0 3 6
Halton-Peel 5 13 6 14 14 48 5 11 11 31 6 13 2 4 2 8 1 1 8 17
Huron-Perth 5 12 6 16 12 44 4 11 12 27 3 7 2 4 2 10 1 1 7 18
Kingston-Prince Edward 4 9 5 10 10 32 5 12 9 23 4 8 2 4 2 8 1 1 5 11
London-Middlesex 5 14 6 16 12 45 4 12 12 27 5 11 2 4 2 9 1 1 7 18
Manitoulin-Northshore-Killarney 1 4 0 0 6 18 2 4 1 3 0 0 1 1 0 0 0 0 2 4
Niagara 5 13 5 13 13 45 5 11 10 29 4 11 2 4 2 8 1 1 6 16
North Bay-West Nipissing 1 4 2 4 7 20 2 4 1 3 0 0 1 1 0 0 0 0 2 4
Oxford-Brant 5 14 6 16 13 46 5 11 12 31 4 11 2 4 2 8 1 1 6 16
Parry Sound-Muskoka-Huntsville 4 10 5 11 10 30 4 10 8 21 2 5 2 4 1 4 0 0 5 10
Peterborough-Kawartha Lakes 5 12 6 12 12 38 4 10 8 21 3 6 2 4 2 8 0 0 6 13
Prescott and Russell 3 5 1 1 7 25 2 5 2 4 1 1 2 4 1 2 0 0 1 2
Renfrew-Pembroke-Barry’s Bay 2 4 3 6 5 17 1 3 2 5 0 0 2 4 1 2 0 0 1 2
Sarnia-Lambton 5 14 6 16 13 46 4 12 13 29 4 10 2 4 2 10 2 4 7 18
Sault Ste. Marie-Superior East 1 5 0 0 4 10 1 3 1 3 0 0 0 0 0 0 0 0 1 3
Simcoe-Delhi-Norfolk 5 14 6 16 13 46 5 11 12 31 4 11 2 4 2 10 1 1 6 16
Smiths Falls-Lanark-Sharbot Lake 3 7 4 8 6 19 2 5 2 4 1 1 2 4 1 2 0 0 1 2
Stirling-Tweed-South Frontenac 5 12 5 10 8 25 2 5 5 13 2 3 2 4 2 8 0 0 3 6
Waterloo-Wellington 5 12 5 13 13 45 5 11 11 29 3 7 2 4 2 8 1 1 6 15
Windsor-Essex-Chatham-Kent 6 17 6 16 13 46 4 14 13 38 5 12 3 5 2 10 4 8 8 24
York-Durham 5 12 6 14 14 48 5 11 11 29 5 9 2 4 2 8 1 1 8 16
Ontario 7 19 8 20 15 53 6 17 13 39 8 17 3 5 3 12 5 9 12 30

Note:

A smog advisory day refers to a calendar day when a smog advisory is in effect.

Figure A1: 20 year trend of ozone annual mean at Windsor Downtown

20 year trend of ozone annual mean at Windsor Downtown. Increase in 61 per cent.

Figure A2: 20 year trend of ozone annual mean at Windsor West

20 year trend of ozone annual mean at Windsor West. Increase in 61 per cent.

Figure A3: 20 year trend of ozone annual mean at Sarnia

20 year trend of ozone annual mean at Sarnia. Increase in 32 per cent.

Figure A4: 20 year trend of ozone annual mean at Grand Bend

20 year trend of ozone annual mean at Grand Bend. Increase in 3 per cent.

Figure A5: 20 year trend of ozone annual mean at London

20 year trend of ozone annual mean at London. Increase in 22 per cent.

Figure A6: 20 year trend of ozone annual mean at Tiverton

20 year trend of ozone annual mean at Tiverton. No change.

Figure A7: 20 year trend of ozone annual mean at Kitchener

20 year trend of ozone annual mean at Kitchener. Increase in 22 per cent.

Figure A8: 20 year trend of ozone annual mean at St. Catharines

20 year trend of ozone annual mean at Saint Catharines. Increase in 40 per cent.

Figure A9: 20 year trend of ozone annual mean at Guelph

20 year trend of ozone annual mean at Guelph. Increase in 27 per cent.

Figure A10: 20 year trend of ozone annual mean at Hamilton Downtown

20 year trend of ozone annual mean at Hamilton Downtown. Increase in 66 per cent.

Figure A11: 20 year trend of ozone annual mean at Hamilton Mountain

20 year trend of ozone annual mean at Hamilton Mountain. Increase in 46 per cent.

Figure A12: 20 year trend of ozone annual mean at Hamilton West

20 year trend of ozone annual mean at Hamilton West. Increase in 42 per cent.

Figure A13: 20 year trend of ozone annual mean at Toronto Downtown

20 year trend of ozone annual mean at Toronto Downtown. Increase in 67 per cent.

Figure A14: 20 year trend of ozone annual mean at Toronto East

20 year trend of ozone annual mean at Toronto East. Increase in 32 per cent.

Figure A15: 20 year trend of ozone annual mean at Toronto North

20 year trend of ozone annual mean at Toronto North. Increase in 33 per cent.

Figure A16: 20 year trend of ozone annual mean at Burlington

20 year trend of ozone annual mean at Burlington. Increase in 17 per cent.

Figure A17: 20 year trend of ozone annual mean at Oakville

20 year trend of ozone annual mean at Oakville. Increase in 39 per cent.

Figure A18: 20 year trend of ozone annual mean at Oshawa

20 year trend of ozone annual mean at Oshawa. Increase in 26 per cent.

Figure A19: 20 year trend of ozone annual mean at Mississauga

20 year trend of ozone annual mean at Mississauga. Increase in 39 per cent.

Figure A20: 20 year trend of ozone annual mean at Dorset

20 year trend of ozone annual mean at Dorset. Decrease in 7 per cent.

Figure A21: 20 year trend of ozone annual mean at Ottawa Downtown

20 year trend of ozone annual mean at Ottawa Downtown. Increase in 34 per cent.

Figure A22: 20 year trend of ozone annual mean at Cornwall

20 year trend of ozone annual mean at Cornwall. Increase in 26 per cent.

Figure A23: 20 year trend of ozone annual mean at Thunder Bay

20 year trend of ozone annual mean at Thunder Bay. Increase in 26 per cent.

Figure A24: 20 year trend of ozone annual mean at Sault Ste. Marie

20 year trend of ozone annual mean at Sault Saint Marie. Increase in 33 per cent.

Figure A25: 20 year trend of ozone annual mean at North Bay

20 year trend of ozone annual mean at North Bay. Increase in 5 per cent.

Figure A26: 20 year trend of ozone annual mean at Sudbury

20 year trend of ozone annual mean at Sudbury. Increase in 1 per cent.

Figure A27: 20 year trend of NO2 annual mean at Windsor Downtown

20 year trend of nitrogen dioxide annual mean at Windsor Downtown. Decrease in 52 per cent.

Figure A28: 20 year trend of NO2 annual mean at Sarnia

20 year trend of nitrogen dioxide annual mean at Sarnia. Decrease in 55 per cent.

Figure A29: 20 year trend of NO2 annual mean at London

20 year trend of nitrogen dioxide annual mean at London. Decrease in 66 per cent.

Figure A30: 20 year trend of NO2 annual mean at Kitchener

20 year trend of nitrogen dioxide annual mean at Kitchener. Decrease in 46 per cent.

Figure A31: 20 year trend of NO2 annual mean at St. Catharines

20 year trend of nitrogen dioxide annual mean at Saint Catharines. Decrease in 48 per cent.

Figure A32: 20 year trend of NO2 annual mean at Hamilton Downtown

20 year trend of nitrogen dioxide annual mean at Hamilton Downtown. Decrease in 42 per cent.

Figure A33: 20 year trend of NO2 annual mean at Hamilton Mountain

20 year trend of nitrogen dioxide annual mean at Hamilton Mountain. Decrease in 51 per cent.

Figure A34: 20 year trend of NO2 annual mean at Toronto Downtown

20 year trend of nitrogen dioxide annual mean at Toronto Downtown. Decrease in 55 per cent.

Figure A35: 20 year trend of NO2 annual mean at Toronto East

20 year trend of nitrogen dioxide annual mean at Toronto East. Decrease in 40 per cent.

Figure A36: 20 year trend of NO2 annual mean at Toronto North

20 year trend of nitrogen dioxide annual mean at Toronto North. Decrease in 33 per cent.

Figure A37: 20 year trend of NO2 annual mean at Burlington

20 year trend of nitrogen dioxide annual mean at Burlington. Decrease in 36 per cent.

Figure A38: 20 year trend of NO2 annual mean at Oakville

20 year trend of nitrogen dioxide annual mean at Oakville. Decrease in 51 per cent.

Figure A39: 20 year trend of NO2 annual mean at Oshawa

20 year trend of nitrogen dioxide annual mean at Oshawa. Decrease in 72 per cent.

Figure A40: 20 year trend of NO2 annual mean at Ottawa Downtown

20 year trend of nitrogen dioxide annual mean at Ottawa Downtown. Decrease in 59 per cent.

Figure A41: 20 year trend of SO2 annual mean at Windsor Downtown

20 year trend of sulfur dioxide annual mean at Windsor Downtown. Decrease in 51 per cent.

Figure A42: 20 year trend of SO2 annual mean at Windsor West

20 year trend of sulfur dioxide annual mean at Windsor West. Decrease in 62 per cent.

Figure A43: 20 year trend of SO2 annual mean at Sarnia

20 year trend of sulfur dioxide annual mean at Sarnia. Decrease in 45 per cent.

Figure A44: 20 year trend of SO2 annual mean at Hamilton Downtown

20 year trend of sulfur dioxide annual mean at Hamilton Downtown. Decrease in 39 per cent.

Figure A45: 20 year trend of SO2 annual mean at Hamilton Mountain

20 year trend of sulfur dioxide annual mean at Hamilton Mountain. Decrease in 50 per cent.

Figure A46: 20 year trend of SO2 annual mean at Ottawa Downtown

20 year trend of sulfur dioxide annual mean at Ottawa Downtown. Decrease in 85 per cent.

Figure A47: 20 year trend of SO2 annual mean at Sault St. Marie

20 year trend of sulfur dioxide annual mean at Sault Saint Marie. Decrease in 55 per cent.

Figure A48: 20 year trend of SO2 annual mean at Sudbury

20 year trend of sulfur dioxide annual mean at Sudbury. Decrease in 69 per cent.

Acknowledgements

This report has been prepared by the staff of the Environmental Monitoring and Reporting Branch of the Ontario Ministry of the Environment and Climate Change. Environment Canada’s National Air Pollution Surveillance program is acknowledged for providing air monitoring instrumentation to the province of Ontario.

For more information:

Ministry of the Environment and Climate Change Public Information Centre

Email: picemail.moe@ontario.ca
Website: Ministry of the Environment and Climate Change

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