AIR QUALITY
Indicators
- Air Composition*
- Air Emissions*
- Air Deposition
* Trend graphs are available for indicators highlighed in orange.
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Trend Graphs (NEW)
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Indicators
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Trend Graphs
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Air Composition
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- Trends in Atmospheric Carbon Dioxide Levels at Monitoring Stations in Hawaii and Nunavut (PDF: 62 KB)
- Annual Average Total Suspended Particulate in Yellowknife and Number Exceedances of Daily Standard
(PDF: 104 KB)
- Annual Average SO2 in Yellowknife and Number of Exceedances of Hourly Standard (PDF: 252 KB)
- Yellowknife Air Quality Data – Annual TSP, Pm2.5, PM10, arsenic, sulphur dioxide, ozone, nitrogen dioxide, carbon monoxide (PDF: 107 KB)
- Inuvik Air Quality – Sulphur dioxide, nitrogen dioxide, PM2.5, ozone
(PDF: 41 KB)
- Fort Liard Air Quality – Sulphur dioxide, PM 2.5, nitrogen dioxide (PDF: 33 KB)
- Norman Wells Air Quality – Sulphur dioxide, nitrogen dioxide, PM2.5, ozone
(PDF: 50 KB)
- World Ozone and Ultraviolet Radiation Data Centre (WOUDC) (Web site)
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Air Emissions
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Current Knowledge
Uninhabited areas of the NWT are considered to have pristine air. Air quality in developed regions such as Yellowknife, is compared to "natural" levels found within these regions.
Community emission sources include power generation, residential and commercial heating, transportation and incineration of waste, including medical waste. Peak pollution concentrations occur in the springtime due to dust from roads and on cold winter days when pollutants are trapped near the surface.
Mining emission sources include power generation, mine fleet, ore processing and remote camp wastes. Air quality modelling completed during Environmental Assessments indicates that there is potential for local air quality impacts during development. Dust appears to be the main concern. Most mines have, or are developing, an air quality monitoring program. Ongoing modelling studies are investigating cumulative impacts from mine emissions to regional air quality.
Oil and gas emission sources include flares, power generation, compressors, line heaters, pump jacks , dehydrators and remote camp wastes. The potential for air quality impacts depends on the size and location of the facility, the composition of the gas or oil being extracted and the type of fuel used at the facility.
Smoke from forest fires can greatly affect local and regional air quality. Forest fires can cause high concentration levels of particulate matter and ground-level ozone and can significantly impact visibility. Most exceedances of air quality standards in the NWT are linked to forest fires.
Current Monitoring
- Air quality monitoring stations (6) – Government of the Northwest Territories (GNWT)
- Upper air monitoring program – Environment Canada
- Air quality monitoring program - BHP Diamonds Inc.
- Dust Monitoring - Diavik Diamond Mines Inc.
- Air quality monitoring program – Snap Lake – DeBeers Inc.
- Air quality monitoring program – Paramount Cameron Hills Oil and Gas
Gaps and Recommendations
Monitoring sites are needed in Fort Liard, Norman Wells and Inuvik. These sites would measure cumulative amounts - those amounts from all activity and development combined.
There is a lack of cumulative regional air quality monitoring. Measurements at Daring Lake should begin again and continue in order to assess changes in air quality from diamond mining activities. A new air quality station should be established downwind of the diamond mines to help determine cumulative impacts from mine activities.
Gather and record information about incineration activities at remote camps.
Source: A Preliminary State of Knowledge of Valued Components for the NWT Cumulative Impact Monitoring Program (NWT CIMP) and Audit - Final Draft. February 2002; updated February 2005 and June 2007.
For more details, you may also want to look at:
- Air Quality
Excerpt
- VC State of Knowledge Full
Report
- NWT Environmental Audit 2005 - Supplementary Report on the Status of the Environment
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