Indicator: A-27 Concentration of nitrogen dioxide in regional areas
Data
| 1991 | 1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Newcastle - NSW | 0.076 | 0.07 | 0.049 | 0.044 | 0.048 | 0.039 | 0.049 | 0.044 | 0.04 | ||
| Wallsend NSW | 0.067 | 0.048 | 0.057 | 0.044 | 0.058 | 0.035 | 0.034 | 0.054 | 0.044 | ||
| Albion Park NSW | 0.044 | 0.081 | 0.049 | 0.055 | 0.051 | ||||||
| Wollongong NSW | 0.09 | 0.074 | 0.066 | 0.081 | 0.064 | 0.058 | 0.062 | 0.065 | 0.056 | ||
| Geelong Vic | 0.063 | 0.054 | 0.063 | 0.063 | 0.048 | 0.044 | 0.067 | 0.046 | 0.048 | 0.047 | |
| Traralgon Vic | 0.04 | 0.042 | 0.054 | 0.032 | 0.04 | 0.035 | 0.041 | 0.036 | 0.042 | 0.041 | 0.033 |
| Moe Vic | 0.043 | 0.045 | 0.048 | 0.034 | 0.031 | 0.027 | 0.036 | 0.049 | 0.049 | 0.05 | 0.038 |
| Helensvale Qld | 0.047 | 0.041 | 0.05 | 0.043 | |||||||
| Barney Point Qld | 0.086 | 0.086 | 0.068 | 0.053 | 0.047 | 0.05 | 0.042 | 0.092 | 0.036 | 0.062 | 0.041 |
| South Gladstone Qld | 0.048 | 0.06 | 0.049 | 0.038 | 0.045 | 0.031 | 0.022 | 0.034 | 0.031 | 0.048 | |
| Hope Valley WA | 0.049 | 0.034 | 0.042 | 0.047 | 0.033 | 0.045 | 0.033 | 0.044 | 0.032 | 0.033 | 0.033 |
| Rockingham WA | 0.02 | 0.041 | 0.033 | 0.043 | 0.03 | 0.048 | 0.046 | ||||
| Rolling Green WA | 0.028 | 0.028 | 0.035 | 0.022 | 0.035 | 0.029 | 0.024 | 0.027 | 0.026 | ||
| Dampier WA | 0.018 | 0.021 | 0.23 | ||||||||
| NEPM 1-hour standard | 0.12 | 0.12 | 0.12 | 0.12 | 0.12 | 0.12 | 0.12 | 0.12 | 0.12 | 0.12 | 0.12 |
Source: Table A4.9 (p.208) of State of the Air Report
What the data mean
All regional monitoring sites show either a decrease in or fairly constant levels of nitrogen dioxide concentrations over the reporting period, 1991 to 2001. All sites meet the National Environment Protection Measure standard for nitrogen dioxide concentrations.
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
Nitrogen dioxide is formed in the ambient air through the oxidation of nitric oxide and plays an important role in the formation of photochemical smog. The major sources of nitrogen oxides are motor vehicles and industry, especially power plants.
The health effects of short-term exposure to nitrogen oxide include respiratory illnesses in children. Long-term exposure may lower resistance to respiratory infections.
Excessive levels of nitrogen dioxide can cause death in plants and roots and damage to the leaves of many agricultural crops. Excessive levels increase the acidity of rain (lower the pH) and thus lower the pH of surface and groundwaters as well as soils. In turn, this lowered pH can have harmful effects, including death, on a variety of biota. Atmospheric concentrations of nitrogen dioxide 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-28 Concentrations of sulphur dioxide in regional areas
- A-29 Concentrations of Particles PM10 and PM2.5 in regional areas
- A-30 Concentration of benzene in regional areas
- LD-26 Dust storm index
Human Settlements — Liveability of human settlements - Air quality
Nitrogen dioxide is formed in the ambient air through the oxidation of nitric oxide and plays an important role in the formation of photochemical smog. The major sources of nitrogen oxides are motor vehicles and industry, especially power plants.
The health effects of short-term exposure to nitrogen oxide include respiratory illnesses in children. Long-term exposure may lower resistance to respiratory infections.
Excessive levels of nitrogen dioxide can cause death in plants and roots and damage to the leaves of many agricultural crops. Excessive levels increase the acidity of rain (lower the pH) and thus lower the pH of surface and groundwaters as well as soils. In turn, this lowered pH can have harmful effects, including death, on a variety of biota. Atmospheric concentrations of nitrogen dioxide 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-28 Concentrations of sulphur dioxide in regional areas
- A-29 Concentrations of Particles PM10 and PM2.5 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
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