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07/2398 - Revised Noise Report and cover letters to referral agencies [As Published] · 132007.2398
RSL Care Proposed RSL Retirement Village, Cooroy - Road and Rail Noise Assessment (Revised) == 3 BASELINE NOISE MONITORING 3.1 SELECTION OF MONITORING POSITION Two attended noise monitoring positions were chosen for the purposes of the assessment. The first monitoring position was located at the development site boundary adjacent to the Cooroy Connection Road. The noise monitoring position has a direct line of sight to the railway and road, hence was unobstructed from vehicular and train noise emissions. Attended noise measurements were also completed at this location for determining maximum noise levels associated with passing trains. The second monitoring position was located at the rear of the development site, at the end of Trading Post Road. The purpose of the noise monitoring was to determine to typical background noise levels experienced by nearby residents which have a potential to be impacted by the proposed retirement village. The monitoring locations are depicted on Figure 1 in Appendix A and Plate 1 in Appendix C. 3.2 METHODOLOGY FOR NOISE MONITORING Noise measurements were made using an Acoustic Research Laboratories environmental noise logger (ARL215). The serial number and calibration information for each instrument is presented in Table 3.1. An averaging time of 15 minutes was adopted and measurements were made over at least a 24-hour period as detailed below. The microphone was positioned at a height of 1.2 m above ground level and fitted with a windshield throughout the measurements. TABLE 3.1: BACKGROUND NOISE MONITORING NATA Field Field Instrument Serial Calibration Calibration Calibration Date of Number Current Until Pre-Check Post-Check Monitoring Level Level ARL noise logger 04/07/2007 - (Monitoring Position 1) 94520 27/09/2008 94.0 dB(A) 94.0 dB(A) 05/07/2007 ARL noise logger 05/07/2007 — (Monitoring Position 2) 94520 27/09/2008 94.0 dB(A) 94.6 dB(A) 09/07/2007 Noise measurements for trains passing by the development site were also completed by Air Noise Environment during a site visit on 4 July, 2007. Measurements were made using a Type 2 Svantek 943AE sound level meter (Serial Number 5163) and calibrator (Serial Number 358). Details of the NATA certified calibrations of these instruments are presented in Table 3.2. AJR NOISE ENVIRONMENT PTY LTD INETWORK/PROJECTS/1750/REPORTING/2008 REVISION/1750REPORT04.ODT Page 5
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