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MCU10/2083 Information Request Response 37 Gibson Rd Noosaville
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Proposed Commercial Development 37 Gibson Street Noosaville ENVIRONMENTAL NOISE IMPACT ASSESSMENT 26906 R09 37 Gibson Rd Noosaville ENV ttp Q TTM Consulting Pty Ltd 2010 7. ANALYSIS 7.1. Source Noise Levels Table 4 shows the source levels that form the basis of the noise predictions. Table 4: Source noise levels Measured Level Correction Corrected Level Noise Source dB(A) LAmax at I m Factor dB(A) * LAmax d6 A Car door closure 77 + 2 (impulsive) 79 Car starting 79 + 2 (impulsive) 81 Car bypass 5 km/h 78 N/A 78 Goods Delivery 85 N/A 85 Waste collection 92 + 2 (impulsive) 94 Conversation 75 N/A 75 77 + 2 (impulsive) 79 *Correction due to tonality and impulsiveness as per AS1055:1997. 7.2. Predicted Noise levels The source levels from Table 4 are used to determine the noise predictions at the nearest affected receivers. The following corrections were applied in calculating the predicted noise impacts: • Distance correction at -6dB per doubling of distance from the source (i.e. 20 x Log(source distance m /receiver distance m). • Most likely source locations were determined from the proposed site plan (i.e. car spaces, etc). • Barrier reductions were determined with a path difference calculation. 2.8m was the assumed height of the proposed building. Point source calculations are displayed in Appendix C. Table 5: Predicted noise impact levels from onsite activities to Receiver I Predicted Level Assessment Criteria dB(A) LAmax Complies Yes/No Noise Source Day Evening Facade 60dB(A) 54dB(A) Car Door Closure 47 Yes Yes Car Passby 49 Yes Yes Car Start 47 Yes Yes Delivery 53 Yes Yes Waste collection 62 +2 dB(A) +8 dB(A) Conversation (front of shops) 44 Yes Yes Conversation (behind shops) 44 Yes Yes Conversation (tenancy 1 deck) 35 Yes Yes Conversation (tenancy 8 deck) 44 Yes Yes Small bin lid closure 38 Yes Yes Page 11
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