Monitoring the environment

2011 Victorian air monitoring results


The general air quality in the Port Phillip (Melbourne and Geelong area) and Latrobe Valley regions in 2011 was good overall, although some areas experienced poorer air quality due to local sources (e.g. Brooklyn). This assessment was based on the air monitoring data measured by EPA’s air monitoring network designed to represent the general air quality in areas of the region. Major impacts on air quality during the year were associated with particles from local dust, urban emissions and smoke from bushfires and planned burns.

Particles as PM10 was the only pollutant measured above the Ambient Air Quality National Environment Protection Measure (AAQ NEPM) air quality standard. For the second time, the Port Phillip Region in 2011 (2010 was the first) met the AAQ NEPM goal of not exceeding the particles as PM10 air quality objective on 5 days at one monitoring site since AAQ NEPM reporting commenced in 2002. This is most likely due to the increased rainfall resulting in less fire and raised dust activity producing less PM10 impacts.  

Unlike the general air quality in Melbourne the local air quality in Brooklyn was regularly impacted by particles as PM10 due to dust emissions from the local industrial estate. Targeted short term air monitoring in Brooklyn designed to assess local impacts measured levels of particles as PM10 above the air quality standard on 13 days during the year.

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Q&A on the 2011 Victorian air monitoring results + Expand all Collapse all

  • Where does EPA monitor?

    In 2011, EPA Victoria monitored air quality at 15 sites across Victoria, with:

    • 13 in metropolitan Melbourne (11 long-term and two short-term)
    • two in Geelong
    • one in the Latrobe Valley.

    Port Phillip region

    Port Phillip Region

    Air monitoring stations around Victoria

    Victorian monitoring stations

  • How do we assess air quality

    Air quality is assessed against the national and/or state objectives and goals shown in the table below.

    Table: State and national air quality objectives and goals

    Pollutant Averaging period Objective Goal to be achieved by 2008 (maximum number of days
    not meeting the objective)
    Particles as PM 10 1 day 50 μg/m3 5 days a year
    Particles as PM2.5 1 day 25 μg/m3 not applicable
    1 year 8 μg/m3
    Visibility-reducing particles 1 hour 20 km 3 days a year
    Ozone 1 hour 0.10 ppm 1 day a year
    4 hours 0.08 ppm 1 day a year
    Carbon monoxide 8 hours 9.0 ppm 1 day a year
    Nitrogen  dioxide 1 hour 0.12 ppm 1 day a year
    1 year 0.03 ppm none
    Sulfur dioxide 1 hour 0.20 ppm 1 day a year
    1 day 0.08 ppm 1 day a year
    1 year 0.02 ppm none
    Lead 1 year 0.50 μg/m3 none
  • What factors affected air quality?

    Air quality in 2011 was mainly affected by: 

    • Local dust, smoke from bush fires and planned burning.
    • Urban sources, predominantly motor vehicle and wood heater emissions accumulating in stable atmospheric conditions. These stable conditions tend to occur on calm, cold autumn/winter nights. These urban sources typically impact visibility more than PM10. When not properly managed, sources such as wood heaters can have a significant local impact.
    • Local sources and emissions from activities such as dust from the Brooklyn Estate.
  • What happened in my region?

    An assessment against Victoria’s air quality objectives and goals is shown in the 2011 data tables (PDF 306 KB)

    In Melbourne the general air quality was good overall.  Major impacts on air quality during the year were associated with particles from local dust and urban emissions (particularly from motor vehicles and wood heaters) that were trapped in calm, highly stable conditions.

    Particles as PM10 was the only pollutant measured by EPA’s air monitoring network above the Ambient Air Quality National Environment Protection Measure (AAQ NEPM) air quality standard. The 24-hour reporting standard for PM2.5 was not exceeded. The air quality standards for nitrogen dioxide, carbon monoxide, sulfur dioxide and ozone were met on all days in 2011 (where there was sufficient data to demonstrate compliance).

    Over all of the monitoring sites, 3 days were measured above the air quality standard for particles as PM10. The 3 days exceeding the PM10 standard in the Port Phillip Region were May 19 – Geelong South; May 20 – Geelong South and Mooroolbark; and June 1 – Alphington. All were attributed to urban sources, typically from vehicle traffic or domestic wood heaters.

    For the second time, the Port Phillip Region in 2011 (2010 was the first) met the AAQ NEPM goal of not exceeding the particles as PM10 air quality objective on 5 days at one monitoring site since AAQ NEPM reporting commenced in 2002.

    Low visibility generally occurring for one to a few hours on a day was measured across Melbourne exceeding the standard at all sites with the highest frequency of events measured at Mooroolbark (18 days). This was a significant improvement on 2010 (36 days). The goal for visibility was not met at all sites. This was mainly caused from small particle emissions such as PM2.5 from bushfires and/or planned burning and urban emissions.

    Unlike the general air quality in Melbourne the local air quality in Brooklyn was regularly impacted by particles as PM10 due to dust emissions from the local industrial estate. Targeted short term air monitoring in Brooklyn and Sunshine West designed to assess local impacts measured levels of particles as PM10 above the air quality standard on 13 days during the year in Brooklyn. This was a significant improvement on 2010 (36 days) due in part to strategies put in place to reduce PM10 dust emissions from the estate. One day was measured above the standard at Sunshine West.

    In 2011 air toxics monitoring was conducted at residential sites in Tullamarine beside the old Tullamarine landfill. The majority of the air toxics were detected at low levels or not at all.

    Tullamarine landfill community air monitoring program – Reports three and four

    Also in 2011 air toxics monitoring was conducted in residential sites at residential sites surrounding the Dandenong South industrial precinct. The results show that for many substances the levels that were monitored were below detectable level. All substances at measurable levels in residential areas were less than the relevant air quality standards.

    In Geelong there were two days where the levels of PM10 exceeded the air quality standard attributed to local windblown dust and low visibility was measured on seven days. The air standards for ozone, nitrogen dioxidecarbon monoxide and sulfur dioxide were all met.  

    In the Latrobe Valley, there were no days where the PM10 air quality standard was exceeded and low visibility events measured on 13 days. This was a significant improvement on 2010 (26 low visibility days). Low visibility days were caused mainly by the accumulation of smoke from planned burns and/or agricultural burning and urban emissions, such as smoke from wood fires in the colder months. Levels of ozone, nitrogen dioxide and sulfur dioxide were measured below the air standards on all days during the year.

    There was no monitoring in other rural regions in 2011.

  • What are the long-term trends?

    Apart from periods of elevated levels of PM10 due to impacts from fire and windblown dust, air quality has changed very little in Melbourne over the past decade. Melbourne’s air quality is considered to be relatively good for a major metropolitan centre.

    Long-term trend graphs are available with the 2011 data tables (PDF 306 KB). Since 2002 the major impacts were influenced by fire generated during major bush fires in 2003, 2006, and 2009, planned burns during 2008 and 2009 and general windblown dust due to the effects of drought and the long-term drying pattern in Victoria.

    For the first time since AAQ NEPM reporting commenced in 2002, the Port Phillip Region met the AAQ NEPM goal of not exceeding the particles as PM10 air quality standard on five days at one monitoring site. The increased rainfall during 2010 reduced the impacts from smoke and windblown dust, contributing to the lower levels of PM10.

    Further analysis of trends in compliance with the air quality goals is given in Air monitoring report 2011 – Compliance with the National Environment Protection (Ambient Air Quality) Measure (publication 1483).

  • How does Melbourne compare with other cities?

    Melbourne's air quality is better than or comparable to interstate and international cities in countries of a similar level of development to Australia. Improvements are necessary, however, to preserve Melbourne's relatively good air quality given increasing pressures from population and economic growth and a changing climate. A comparison is presented in EPA's report on Victoria's air quality in 2006. (PDF 521KB)

Page last updated on 17 Sep 2014