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MINOR CHANGE - Attachment 5 - Noise Impact Assessment.pdf
will be retained, which will see increased activity for the purpose of the hotel and its noise level has been
adjusted accordingly to reflect the increased usage. Data used for modelling noise levels is below:
◼ Carpark movement (#13  in Figure 3.1): 73.7 dBA Lw,eq (15 km/h, 0.5m height)
◼ Carpark movement (#34 (North) in Figure 3.1): 55.0 dBA Lw,eq (15 km/h, 0.5m height)
◼ Carpark movement (#15 & #34 (South) in Figure 3.1): 62.9 dBA Lw,eq (15 km/h, 0.5m height)
◼ Door slams (2 slams per spot per hour): 53.9 dBA Lw,eq (1m height)
◼ The number of vehicle movements used in the calculations is the total number of car movements per car
spaces with half entering and half leaving in an hour period.
It is noted that any door slam carpark activity that is enclosed or located underground has been omitted from
the model since the noise contribution from those carparking spots is expected to be negligible. The modelled
noise sources are illustrated in Figure 6.3.
Figure 6.3: Carpark Noise Source Model
The carparking noise has been modelled and the noise emission results are shown in Table 6.5. While the
previous report assessed each carpark section individually, this report will assess the cumulative impact of all
carpark activity on the nearby receivers.
Table 6.5: Carpark Noise Level Predictions
Noise Source Predicted Noise Limit LAeq,adj,T Exceedance LAeq,adj,T
Noise Level dBA dBA
Leq dBA
R1 R2 R3 Day Evening Night Day Evening Night
Carpark Activity (Cumulative) 27 20 18 39 34 28 nil nil nil
As seen in Table 6.5, noise generated by the carparks are predicted to comply with the anointed noise limits.
Additionally, the carpark noise model is somewhat conservative as it assumes equal levels of activity during
207401.0104.R01V06 Page 13
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