2016-03-09
ANSWER
The modelling undertaken by AECOM Australia is consistent with that required by the Environment Protection Authority (EPA) Victoria. The EPA Victoria's State Environment Projection Policy — Air Quality Management 2001 (SEPP-AQM) specifies that proposed transport corridors must be assessed using one of the regulatory models for near-road modelling or as approved by the EPA Victoria.
The model applied in the assessment, CAL3QHCR, is a steady-state Gaussian dispersion model, designed to determine near-road air pollution concentrations at receptor locations downwind of highways.
The model was specifically approved for use in the CityLink Tulla Widening project by the EPA Victoria.
Modelling shows noise and air pollution will be no more than it currently is. These results have been shared with the college.
SEPP-AQM provides that the background concentrated for the development should be the 70th percentile of one year's observed concentrations. The assessment has applied the 75th percentile, a stricter level than required. Further, the maximum 75th percentile was conservatively applied from not one but five previous years.
The model accounted for hour-by-hour variability in vehicle count, vehicle emissions, fleet composition (both vehicle type and fuel) and meteorology, including identifying and modelling morning and afternoon peak traffic details.
Key assumptions applied in the assessment were specifically chosen to produce conservative predictions and do not account for improvements in technology, such as associated with likely future reductions in vehicle emissions.
The assessment did not account for the positive influence that noise barriers are likely to have on reducing roadside pollutant concentrations.
The model was based on free-flowing traffic along CityLink and on/off ramps connecting with CityLink. The model did not include slow-moving traffic queuing at on-ramps or slow-moving traffic at peak times because the main line CityLink traffic volumes are significantly higher than on/off ramps and would therefore have a higher mass emission of pollution.
Air quality information from Footscray was used because Footscray is the closest EPA Victoria monitoring station to the project. It is worth noting that the Footscray site is located close to the port industrial area as well as Melbourne's central business district, so measured levels at this site are expected to be higher than those likely at Bulla Road. As such, its use in the model is considered conservative.
Modelling of the following pollutants was undertaken: NO2, PM10 and CO. A qualitative assessment of PM2.5 was also made.
PM2.5 is a subset of PM10, which was measured. The emissions of PM2.5 cannot exceed that of PM10. Therefore, because the PM10 levels did not exceed the PM2.5 standard, the PM2.5 levels would not be exceeded. As such, PM2.5 was not originally modelled. A review of modelling data shows that PM10 emissions at Strathmore Secondary College would be approximately 25 per cent lower than the reported maximums in the model. This is because the maximum receptors are generally the receptors closest to the designated section of highway, and the college is set back from the freeway compared to other receptors.
Ozone was not considered because it is not emitted from vehicles during the combustion of vehicle fuel. Sulfur dioxide was not measured because the EPA Victoria report Future air quality in Victoria (2013) identified that sulfur dioxide concentrations were “extremely low in Melbourne, and this is expected to remain the case”. The allowable sulfur content in fuel standards legislated by the Federal Government has and will continue to decrease with time. Lead was not measured because it was effectively phased out of vehicle fuel on 1 January 2002 by the Federal Government.