Indicator: A-29 Concentrations of Particles PM10 and PM2.5 in regional areas
Data
| 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Beresfield NSW | 5 | 9 | 6 | 6 | 0 | 0 | 1 | 3 | |||
| Albion Park NSW | 2 | 5 | 0 | 2 | 1 | ||||||
| Wollongong NSW | 5 | 4 | 3 | 2 | 1 | 0 | 3 | 4 | |||
| Albury NSW | 0 | ||||||||||
| Bathurst NSW | 0 | 0 | |||||||||
| Tamworth NSW | 0 | 0 | |||||||||
| Wagga Wagga NSW | 2 | ||||||||||
| Helensvale Qld | 0 | 0 | 5 | 0 | |||||||
| South Gladstone Qld | 4 | 4 | |||||||||
| Bunbury WA | 0 | 0 | 1 | ||||||||
| Dampier WA | 0 | 3 | 18 |
Source: Table A4.40 (p.257) of State of the Air Report
| 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Beresfield NSW | 81.6 | 66.2 | 100.6 | 71.8 | 46.2 | 48 | 53.6 | 81 | |||
| Albion Park NSW | 61.6 | 63.6 | 48.8 | 62.5 | 58.7 | ||||||
| Wollongong NSW | 104.1 | 61.1 | 69.6 | 64.8 | 56.9 | 40.2 | 58.1 | 68.2 | |||
| Albury NSW | 28.8 | ||||||||||
| Bathurst NSW | 35.2 | 35.6 | |||||||||
| Tamworth NSW | 21.1 | 34.6 | |||||||||
| Wagga Wagga NSW | 69.8 | ||||||||||
| Helensvale Qld | 40.2 | 37.4 | 86.8 | 39.6 | |||||||
| South Gladstone Qld | 65.2 | 66.7 | |||||||||
| Bunbury WA | 40 | 42.4 | 57.6 | ||||||||
| Dampier WA | 44 | 79.5 | 107.7 | ||||||||
| NEPM 24 hour standard | 50 | 50 | 50 | 50 | 50 | 50 | 50 | 50 | 50 | 50 | 50 |
Source: Table A4.41 (p.258) of State of the Air Report
| 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Beresfield NSW | 18.5 | 21.4 | 34.1 | 66.4 | |||||||
| Wollongong NSW | 18.8 | 19.4 | 31.1 | 53.4 | |||||||
| Bunbury WA | 35.4 | 33.2 | 30 | 29.2 | 47.3 | ||||||
| NEPM 24 hour advisory reporting standard | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 | 25 |
Source: Table A4.56 (p.276) of State of the Air Report
| 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Beresfield NSW | 0 | 0 | 2 | 9 | |||||||
| Wollongong NSW | 0 | 0 | 1 | 2 | |||||||
| Bunbury WA | 5 | 3 | 1 | 3 | 2 |
Source: Table A4.55 (p.275) of State of the Air Report
| 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Newcastle NSW | 0 | 4 | 2 | 1 | 1 | 0 | 0 | 0 | 1 | ||
| Beresfield NSW | 1 | 3 | 4 | 2 | 1 | 0 | 0 | 0 | 1 | ||
| Wollongong NSW | 0 | 1 | 1 | 0 | 0 | 0 | 0 | 0 | 1 | ||
| Albion Park NSW | 1 | 2 | 0 | 3 | 0 | ||||||
| Kembla Grange NSW | 5 | 5 | 2 | 2 | 2 | 0 | 3 | 2 | |||
| Wollongong NSW | 0 | 5 | 1 | 0 | 0 | 0 | 0 | 0 | 1 | ||
| Launceston (Ti-Tree Bend), Tas | 27 | 25 | 7 | 15 | 9 | 51 | 47 | 43 | 39 | 28 | |
| Whyalla, SA | 7 | 10 | 3 | 2 | 5 | 3 | 2 | 3 | 7 |
Source: Table A4.46 (p.263) of State of the Air Report
What the data mean
Data is presented for both ‘inhalable particles’ (PM10) and ‘respirable particles’ (PM2.5). Using the TEOM measurement method, there are three locations of particular interest for PM10; Beresfield and Wollongong in New South Wales and Dampier in Western Australia. All of these have exceeded the 24 hour National Environment Protection Measure standard of 50 ug/m3 on several occasions over the reporting period, 1991 to 2001. In 2001, Dampier exceeded the standard on 18 days. However, using the HiVol method, Launceston in Tasmania had a very high exceedence level, mostly due to woodsmoke.
While there is no enforceable National Environment Protection Measure standard as of yet for PM2.5, there is a 24 hour advisory reporting standard of 25 ug/m3. There are three locations of particular interest for PM2.5; Beresfield, Wollongong and Bunbury in Western Australia. The most significant of these is the Beresfield, which is located near the industrialised area of Newcastle.
Data Limitations
Comparisons of historical data sets across the nation are difficult due to lack of harmonisation in network designs, and in sampling, analysis, quality control and reporting practices. In addition, discontinuities and changes in data collection and reporting practices can distort trend analysis results.
Issues for which this is an indicator and why
Atmosphere — Air quality - Regional air quality
Particles less than 10 micrometres (µm) are referred to as PM10 and are called ‘inhalable particles’. Particles less than 2.5µm are known as PM2.5 or ‘respirable particles’.
The main sources of include motor vehicles, domestic wood heaters, bushfires and controlled burns, wind-blown dust, sea-salt, industrial facilities such as power stations, and photochemical processes.
The specific effects of particulate matter will depend on its composition, concentration and the presence of other pollutants such as acid forming gases. However, particles are associated with increased respiratory symptoms, aggravation of asthma, increased hospitalisation for heart and lung diseases, and premature death in humans and animals. Atmospheric particle concentrations are a direct indicator for this issue.
Other indicators for this issue:
- A-24 Concentrations of carbon monoxide in regional areas
- A-25 Concentrations of ozone in regional areas
- A-26 Concentrations of lead in regional areas
- A-27 Concentration of nitrogen dioxide in regional areas
- A-28 Concentrations of sulphur dioxide in regional areas
- A-30 Concentration of benzene in regional areas
- LD-26 Dust storm index
Human Settlements — Liveability of human settlements - Air quality
Particles less than 10 micrometres (µm) are referred to as PM10 and are called ‘inhalable particles’. Particles less than 2.5 µm are known as PM2.5 or ‘respirable particles’.
The main sources of include motor vehicles, domestic wood heaters, bushfires and controlled burns, wind-blown dust, sea-salt, industrial facilities such as power stations, and photochemical processes.
The specific effects of particulate matter will depend on its composition, concentration and the presence of other pollutants such as acid forming gases. However, particles are associated with increased respiratory symptoms, aggravation of asthma, increased hospitalisation for heart and lung diseases, and premature death in humans and animals. Atmospheric particle concentrations are a direct indicator for this issue.
Other indicators for this issue:
- A-17 Concentrations of carbon monoxide in urban areas
- A-18 Concentrations of ozone in urban areas
- A-19 Concentration of lead in urban areas
- A-20 Concentrations of nitrogen dioxide in urban areas
- A-21 Concentration of sulphur dioxide in urban areas
- A-22 Concentration of Particles PM10 and PM2.5 in urban areas
- A-23 Concentration of benzene in urban areas
- A-24 Concentrations of carbon monoxide in regional areas
- A-25 Concentrations of ozone in regional areas
- A-26 Concentrations of lead in regional areas
- A-27 Concentration of nitrogen dioxide in regional areas
- A-28 Concentrations of sulphur dioxide in regional areas
- A-30 Concentration of benzene in regional areas
- CO-70 Examples or case studies of localised impacts of windborne dust and smoke
Further Information
Key
Links to another web site
Links to data in the DRS
Opens a pop-up window
Before you download
Some documents are available as PDF files. You will need a PDF reader to view PDF files.
List of PDF readers
If you are unable to access a publication, please contact us to organise a suitable alternative format.
