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Long-term unattended noise monitoring<br />

Table 6-17 shows the monitored long-term ambient noise levels across the study<br />

area.<br />

Table 6-17<br />

Summary <strong>of</strong> unattended noise monitoring data for the study area<br />

Report Reference 1<br />

Clarence Street and York<br />

Street<br />

(ref: BPI-Erskine Street)<br />

Daytime 7.00am<br />

6.00pm<br />

Noise level (dB(A))<br />

Evening 6.00pm<br />

10.00pm<br />

Night-time<br />

10.00pm 7.00am<br />

RBL RBL RBL<br />

66 64 57<br />

Erskine Street intersection 63 59 54<br />

(ref: BPI- Clarence Street)<br />

Note 1: BPI denotes a measurement referenced from the Sydney City Centre Bus<br />

Infrastructure.<br />

The above data support the short-term attenuated monitoring, showing a similar<br />

small variation in average long-term noise levels in the <strong>city</strong> <strong>centre</strong> between the<br />

daytime, evening and night time.<br />

Noise sensitive receivers<br />

There is a diversity <strong>of</strong> land uses within the study area (refer to section 6.5.2). They<br />

include high-rise residential buildings, public open spaces and other noise-sensitive<br />

receiver types (eg educational facilities, health facilities and community support<br />

facilities). As a result it was not feasible to assess the impact at every single receiver.<br />

Consequently, a number <strong>of</strong> representative receivers within the study area were<br />

selected. They represented those locations that are the most sensitive to change<br />

(eg those that are located closest to each work site). The receiver locations are<br />

described in Table 6 to Table 16 <strong>of</strong> Appendix D.<br />

Vibration sensitive receivers<br />

Structural building damage can occur up to 15 metres from a vibration source whilst<br />

amenity effects (human comfort) can be experienced up to 100 metres from a<br />

vibration source. Construction vibration impacts could therefore affect any noisesensitive<br />

receivers that are located this distance from the works as well as any<br />

buildings.<br />

6.2.4 Potential impacts<br />

Noise and vibration construction impacts<br />

Construction noise<br />

The noise modelling assessment assumed a typical worst case scenario where the<br />

nosiest equipment (or a combination <strong>of</strong> equipment) would operate at its maximum<br />

output and at the minimum distance between the limit <strong>of</strong> each work site and the<br />

representative noise-sensitive receiver(s) listed in Table 6 to Table 16 <strong>of</strong> Appendix D.<br />

Sydney City Centre Capa<strong>city</strong> Improvement 217<br />

Review <strong>of</strong> Environmental Factors

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