3.                    NOISE

3.1                                      Monitoring Requirement

3.1.1                        In accordance with the Contract Specific EM&A Manuals, Leq (30min) monitoring is conducted for at least once a week during the construction phase between 0700 and 1900 on normal weekdays at the designated monitoring locations.

3.2                                      Monitoring Equipment

3.2.1                                 The sound level meter used in noise monitoring shall comply with the International Electrotechnical Commission Publication (IEC) 651:1979 (Type 1) and 804:1985 (Type 1) specifications as referred to in the Technical Memorandum issued under the Noise Control Ordinance (NCO).

3.2.2                                 Sound level calibrator shall be used for the on-site calibration of the meter. This calibrator complies with the IEC Publication 942 (1988) Class 1 and ANSI S1.40 - 1984. Noise measurements were only accepted to be valid if the calibration levels from before and after the measurement agree to within 1.0 dB(A).

3.2.3                                 Measurements shall be recorded to the nearest 0.1dB(A). Sound level meters are programmed to measure A-weighted equivalent continuous sound pressure level at 30-minute intervals between 0700 and 1900 on normal weekdays at least once a week when construction activities are underway.

3.2.4                                 The model of the noise monitoring equipment used is summarized in Table 3.1.

3.3                                      Monitoring Parameters and Frequency

3.3.1                                 The parameters and frequencies of impact noise monitoring is summarized in Table 3.2.

3.4                                      Monitoring Methodology

3.4.1                                 Noise measurement should be conducted as the following procedures:

 

¡P          Free field measurements was made at monitoring location M-N3. A correction of +3 dB(A) shall be made to the free field measurements.

¡P          The battery condition should be checked to ensure good functioning of the meter.

¡P          Parameters such as frequency weighting, the time weighting and the measurement time should set as follow:

 

(i)               Frequency weighting: A

(ii)              Time weighting: Fast

(iii)             Measurement time: continuous 5 minutes interval

 

¡P          Prior to and after noise measurement, the meter shall be calibrated using the calibrator for 94.0 dB(A) at 1000 Hz. If the difference in the calibration level before and after measurement is more than 1.0 dB(A), the measurement will be considered invalid and repeat of noise measurement is required after re-calibration or repair of the equipment.

¡P          The wind speed at the monitoring station shall be checked with the portable wind meter. Noise monitoring should be cancelled in the presence of fog, rain, and wind with a steady speed exceeding 5 m/s, or wind with gusts exceeding 10 m/s.

¡P          Noise measurement should be paused during periods of high intrusive noise if possible and observation shall be recorded when intrusive noise is not avoided.

¡P          At the end of the monitoring period, the Leq, L10 and L90 should be recorded. In addition, site conditions and noise sources should also be recorded on a standard record sheet.

3.5                                      Maintenance and Calibration

3.5.1                                 Maintenance and calibration procedures should also be carried out, including:

¡P          The microphone head of the sound level meter and calibrator should be cleaned with a soft cloth at quarterly intervals.

¡P          The sound level meter and calibrator should be calibrated annually by a HOKLAS laboratory or the manufacturer.

¡P          The calibration certificates for noise monitoring equipment are provided in Appendix D.

3.6                                      Monitoring Locations

3.6.1                                 In accordance with the Contract Specific EM&A Manual, two noise monitoring locations, namely NMS2 and NMS3C are covered under Contract No. HY/2019/01 ¡§Hong Kong-Zhuhai-Macao Bridge Hong Kong Boundary Crossing Facilities ¡V Phase 2 and Other Works.

3.6.2                                 Due to rejection from Ho Yu College (NMS3) for setting up a noise monitoring station at their school, an alternative location at site boundary of the site office area at Works Area WA2 (NMS3B) is proposed. Impact noise monitoring has been relocated from NMS3B to Ying Tung Estate Market Rooftop (NMS3C) on 20 August 2018 under Contract No. HY/2013/04. The same baseline and Action and Limit levels for noise, as derived from the baseline monitoring data recorded at Ho Yu College, are adopted for this alternative noise monitoring location.

3.6.3                                 The most updated locations are summarized in Table 3.3 and the locations of the noise monitoring stations shown in Figure 3.

3.7                                      Monitoring Results

3.7.1                                 The schedule of noise monitoring in reporting month is provided in Appendix E.

3.7.2                                 No raining and wind with speed over 5 m/s was observed during noise monitoring according to the onsite observation. The weather conditions during the monitoring month are provided in Appendix K.

3.7.3                                 The noise monitoring data are summarized in Table 3.4. Detailed monitoring data are presented in Appendix F.

3.7.4                                 School calendar of Ho Yu College was checked against noise monitoring days at NMS3C. The examination periods of Ho Yu College were 11 November 2021 to 16 November 2021. Therefore, the limit level for NMS3C was 65 dB (A) on 15 November 2021.

3.7.5                                 No Action / Limit Level exceedance of location NMS2 was recorded for construction noise in the reporting month.

3.7.6                                 The measured noise level recorded at NMS3C on 3 November 2021 were 71.1 dB (A), which exceeded the limit level 70 dB (A). The noise level were higher than the baseline level of 66.3 dB (A). Therefore, baseline correction was carried out and the corrected noise levels which solely represent the noise level of construction works was 69.4 dB (A), therefore there was no exceedance after correction. As such the Event and Action Plan was not triggered.

3.7.7                                 During the monitoring month, at NMS3C, road traffic along the Ying Tung Road and non-project related construction activities at the nearby construction site was observed.

3.7.8                                 The Action and Limit Levels for noise impact monitoring have been set and are presented in Appendix C.

3.7.9                                 The Event and Action Plan for noise is given in Appendix H.