An assessment against Victoria’s air quality objectives and goals is shown in the 2008 data tables.
In Melbourne there were fewer days when the particle (PM10 and visibility) objectives were not met, compared with the previous two years. Elevated PM10 levels occurred mainly on days affected by planned burning (in April) and windblown dust (during the warmer months). Low visibility days were caused mainly by planned burning and urban emissions (particularly from motor vehicles and wood heaters) that were trapped in calm, highly stable conditions.
The four-hour ozone objective was exceeded at one coastal station in Melbourne (Point Cook) on two days under conditions suitable for the generation of photochemical smog. The ozone objectives were met at all other stations.
The air quality objectives for nitrogen dioxide, carbon monoxide and sulfur dioxide were met on all days in 2008.
As part of EPA’s monitoring plan for air toxics, benzo(a)pyrene monitoring concluded at Mooroolbark in January 2008 and commenced at Campbellfield in February 2008. Levels were low and met the limits specified in the National Environment Protection Measure (NEPM) for Air Toxics.
In Geelong, there were fewer days when the particle (PM10 and visibility) objectives were not met, compared with the previous two years. As was observed in 2006 and 2007, windblown dust was the major cause of high PM10 levels. Geelong had fewer days that did not meet the visibility objective than most Melbourne stations in 2008. Days of poor visibility were caused mainly by planned burning and urban emissions.
The objectives for ozone, nitrogen dioxide, carbon monoxide and sulfur dioxide were all met.
In the Latrobe Valley, there were fewer days when the particle (particularly PM10 and visibility) objectives were not met, compared with the previous two years. The main causes of high PM10 were smoke from planned burns (in April) and windblown dust. Low visibility days were caused mainly by the accumulation of urban emissions, such as smoke from wood fires (in the colder months) and planned burning.
The objectives for ozone, nitrogen dioxide and sulfur dioxide were met on all days.
Air toxics monitoring at Traralgon concluded in January 2008. Levels were low and met the limits specified in the Air Toxics NEPM.
There was no monitoring in other rural regions in 2008.