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National Fuel Quality Standards Regulation Impact Statement 1 ...

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ecorded in Sydney and Melbourne are comparable with cities such as Toronto, San<br />

Diego, Philadelphia and Atlanta, and exceed those in London.<br />

Until recently, breaches of the standard in most Australian cities have declined steadily.<br />

However, adoption of the more stringent World Health Organisation 1 hour goal<br />

(0.08ppm) would indicate a significantly higher number of recorded exceedences, and a<br />

worsening upward trend. For example, in Sydney the number of exceedences in 1994,<br />

based on 0.12ppm, 0.10ppm and 0.08ppm goals, were 2, 12 and 25 days respectively<br />

(NSW EPA, 1996a). A 1 hour standard of 0.08ppm is the current goal in Western<br />

Australia, and has been identified by NSW as a long term objective (NSW EPA, 1996b).<br />

Fine particles (also referred to as particulate matter or PM) Respirable particles,<br />

those with a diameter of less than 10 µm (PM10), are a particular health concern because<br />

they are easily inhaled and retained in the lung. Almost all of the particles in diesel<br />

exhaust are less than 1 µm in diameter (Concawe, 1998), and diesel particles also adsorb<br />

unburnt hydrocarbons and other potentially carcinogenic organic compounds such as<br />

polycyclic aromatic hydrocarbons. The International Agency for Research on Cancer has<br />

concluded that diesel exhaust is a probable human carcinogen (California Air Resources<br />

Board 1994), and the California Air Resources Board has proposed that diesel exhaust be<br />

classified as a toxic air contaminant (California Air Resources Board, 1998).<br />

Although the mechanisms are not clear, epidemiological studies in the US and elsewhere<br />

consistently show a relationship between particles and a range of respiratory,<br />

cardiovascular and cancer related morbidity and mortality (Concawe, 1996; Ballantyne,<br />

1995; NEPC, 1997). The NSW HARP study estimated that<br />

particle pollution contributed to nearly 400 (2%) premature deaths in Sydney each year<br />

between 1989 and 1993. The study also estimated that days of high particle<br />

concentrations were associated with a 3.5% increase in hospital emissions for<br />

cardiovascular disease, a 3% increase in chronic obstructive pulmonary disease hospital<br />

admissions, and a 3% increase in heart disease admissions in the elderly.<br />

Measurements of PM10 in urban areas indicate that levels are well below current US EPA<br />

standards, but can exceed Californian standards, with annual average levels being around<br />

25 to 40 µg/m 3 and peak 24-hour average levels around 90 to 110 µg/m 3 . Particle<br />

concentrations vary with season, higher values occurring in the autumn/winter months. In<br />

areas where wood smoke from domestic fires dominates, particle levels higher than 150<br />

µg/m 3 (as a 24-hour average) have been recorded on occasion.<br />

2.2 GREENHOUSE GAS EMISSIONS<br />

Scientific evidence points to a discernible human influence on global warming and<br />

climate. There has been a 30% increase in the amount of carbon dioxide in the<br />

atmosphere since the beginning of the industrial revolution, mostly arising from burning<br />

fossil fuels. The earth's temperature has increased during the same period and is now<br />

warmer than at any time during the last 420,000 years.<br />

There are also other effects on climate such as decreasing number of days with frost and<br />

changes to the frequency and intensity of el nino episodes. Though the complex

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