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standard-practice <strong>of</strong> sheeting and covering any trucks and using wheel brushes<br />

would minimise this impact.<br />

Whilst long-term dust exposure can lead to human health impacts, including asthma,<br />

such impacts from this proposal would be unlikely. More likely would be the potential<br />

for localised nuisance in the form <strong>of</strong> minor and temporary dust deposition on outside<br />

dining and seating areas, building frontages and parked cars.<br />

Equipment emissions<br />

Emissions-generating construction equipment (refer to section 3.3.5) may need to<br />

operate within restricted spaces within the <strong>city</strong> <strong>centre</strong> adjacent to building frontages<br />

for a number <strong>of</strong> consecutive days during construction. Whilst it would not impact on<br />

the air quality <strong>of</strong> the road corridor it may have an effect on immediately adjacent<br />

locations where ‘significant numbers <strong>of</strong> people congregate’ (eg ground-floor cafés,<br />

restaurants, hotel lobbies). This would be managed through the controls described<br />

below in Table 6-63.<br />

Emissions associated with construction traffic delays<br />

When traffic idles and queues, engine performance is compromised and fuel burns<br />

less efficiently, leading to an increase in traffic-generate air emissions.<br />

Section 6.1 discusses the consequential minor traffic delays that would occur across<br />

the proposal footprint caused as a result <strong>of</strong> implementing traffic management controls<br />

at each work site during construction. Whilst the construction program and staging<br />

would be used to ensure there would be no effect on the performance <strong>of</strong> the road<br />

network overall, there would be a temporary minor effect on air quality within the<br />

immediacy <strong>of</strong> the affected road corridor due to increased idling traffic. However, as<br />

ambient conditions are significantly below the Air NEPM air quality goals this impact<br />

would have no human health impact despite it potentially being perceptible.<br />

Air quality impacts during operation<br />

Appendix L shows the work sites where traffic flows would increase by more than<br />

1,000 vehicles per day under the proposal. These changes would occur through the<br />

reallocation and reprioritisation <strong>of</strong> traffic within the <strong>city</strong> <strong>centre</strong> as a result <strong>of</strong><br />

implementing the various projects under the Access Strategy. It would occur at<br />

various points within the following work sites:<br />

NW2: King Street<br />

R1: Park Street<br />

R2: Market Street<br />

R4: Clarence Street<br />

R5: York Street<br />

S2: Goulburn Street<br />

S3: Pitt Street<br />

C1: Wentworth Avenue<br />

C2: College Street<br />

F1: Macquarie Street.<br />

As the above screening criterion is triggered at ten <strong>of</strong> the 17 work sites there may be<br />

a perceptible minor reduction in air quality within the immediate road corridor in these<br />

locations. However, as described in the introduction to this section, there may<br />

conversely be a perceptible minor improvement in air quality in other locations due to<br />

the reduction in traffic on certain roads and its reallocation and reprioritisation onto<br />

Sydney City Centre Capa<strong>city</strong> Improvement 399<br />

Review <strong>of</strong> Environmental Factors

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