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Environmental Quality Branch

AIR QUALITY

Air Quality Report for British Columbia: Ground-Level Ozone Concentrations (1986-1997)

Last Updated: July 1998


Executive Summary

Ground-level ozone is an important component of urban smog that is formed from reactions involving nitrogen oxides (NOx) and volatile organic compounds (VOCs) in the presence of sunlight. The motor vehicle is a major source of both NOx and VOCs.

Ozone is a respiratory irritant, and has been associated with a decline in lung function and increased hospitalizations for those with pre-existing respiratory problems. Recent studies indicate that ozone may be causing health effects, even at low concentrations. Ozone is also harmful to plants and to various materials.

Ozone is currently being monitored at more than 25 sites in the province. The monitoring network is most dense in the Lower Fraser Valley (LFV), reflecting both the large population and the high historical ozone concentrations found in this region. Data are forwarded to a central electronic database for storage.

This report provides an overview of provincial ozone levels based on data collected between 1986-1997. Data from 19 sites were evaluated. Site selection was based in part on data availability and on obtaining as broad a geographical cross section of the province as possible. Hence, sites with the worst or the best air quality in the province in any particular year may not have been considered here. Data from each site were summarized in a set of summary plots, an example of which is provided here.

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Note: The (larger) graphs below come from page 35 of the full report — Air Quality Report for British Columbia: Ground-Level Ozone Concentrations (1986-1997).

 

graphic of provincial ozone levels  plotted

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Unless noted otherwise, analyses were based on hourly ozone concentrations. The following observations were drawn from these analyses.

  • There is great temporal and spatial variability in ozone concentrations measured throughout the province.

  • The highest hourly concentrations were observed during the summer months, when conditions are most conducive to ozone formation.

  • During much of the late 1980s, the highest hourly concentrations were observed at sites immediately downwind of the most densely populated areas of the LFV, at sites in Port Coquitlam and Port Moody. Ozone concentrations were particularly high during the summer of 1988, when much of North America was under the influence of a strong high-pressure system that resulted in extended periods of poor air quality. During this period, the Port Coquitlam monitoring site recorded a maximum hourly concentration of 425 µg/m3.

  • More recently, the highest hourly concentrations were recorded in Hope in 1993 (176 µg/m3), Port Coquitlam in 1994 (213 µg/m3), Hope in 1995 and 1996 (188-206 µg/m3), and Kelowna in 1997 (168 µg/m3).

  • On an annual basis, mean hourly concentrations ranged from less than 10 µg/m3 to 45 µg/m3. Over the last five years, the highest mean concentrations were typically monitored at sites further downwind of the more densely populated areas of the LFV (e.g. Surrey, Langley and Hope) and sites outside the LFV (e.g. Victoria, Kamloops, Kelowna, Williams Lake and Prince George).

  • The lowest mean concentrations were consistently observed in Downtown Vancouver (Robson Square), where NOx emissions from vehicle exhaust are likely responsible for the destruction of local ozone.

  • On a monthly basis, the highest hourly mean concentrations were typically observed during the spring months, particularly during April and May. This finding is partly attributed to the increased contributions of stratospheric ozone which occur during the spring, when the stratosphere is closest to the earth's surface. The highest concentrations reported during this period were 60-61 µg/m3 in Kamloops.

  • In contrast, the lowest monthly mean concentrations were typically observed between November and January. Ozone concentrations at Vancouver (Robson Square) averaged less than 10 µg/m3 during this period.

  • The 95th percentile concentration, which represents the level below which 95% of the concentrations fall, is a useful indicator of long-term trends. Although very high hourly concentrations were observed in the late 1980s, a number of sites reported their highest or second highest 95th percentile and mean concentrations in 1996. These sites included Vancouver (Robson Square), Richmond, North Delta, Burnaby (Kensington Park) and Hope. Data from the Hope site indicates that the annual mean concentration consistently increased each year between 1993-96.

  • The national air quality objectives for ozone are currently under review. The current one-hour maximum acceptable level is 160 µg/m3. In the late 1980s, the majority of exceedances of this level occurred in the Port Coquitlam/North Vancouver/Pitt Meadows area. More recently, exceedances have also been observed in Surrey, Langley, Abbotsford, Chilliwack, Hope and Kelowna.

  • In contrast, no exceedances of the air quality objective were recorded in Victoria, Squamish, Vancouver (Robson Square), Kamloops and Prince George between 1986-1997. However, three of the sites (Victoria, Squamish and Kamloops) reported hourly concentrations in excess of 150 µg/m3.

  • A cumulative ozone exposure index, SUM06, was also calculated. SUM06 values are used to assess the exposure of vegetation to ozone during the growing season. A value of 11.6 mg/m3-h over a three-month period is expected to provide protection to 95% of crops. Exceedances of this level were generally limited to the period prior to 1989, with the exception of the Hope site, where exceedances were recorded in 1995 and 1996.

  • Hourly mean, 95th percentile and maximum concentrations observed at various sites in the province in 1997 were compared. Based on this combination of parameters, the highest concentrations were reported for sites in Kelowna and Kamloops. This finding indicates that these sites experience both a high background concentration of ozone throughout the year, and periods of elevated ozone concentrations during the warm, sunny summer months. This finding also suggests that ozone may be an emerging issue in these rapidly growing areas.

  • Eight-hour average concentrations were also calculated. Standards or objectives based on an 8-hour average are believed to provide better protection against longer exposure periods. There are currently no national objectives based on an 8-hour averaging period. However, for comparison purposes, 8-hour average concentrations were evaluated against the U.K. standard of 50 ppb (approximately 100 µg/m3). This level was exceeded at most sites at least once per year, and a maximum of 253 times in Kelowna in 1987.

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For More Information:

Environmental Quality Branch
Ministry of Environment
Government of British Columbia

PO Box 9341, Stn Prov Govt
Victoria, British Columbia
Canada V8W 9M1
http://www.env.gov.bc.ca/air

 
 
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