Contents
Mott MacDonald Hong Kong Limited (MMHK) was commissioned to undertake the Environmental Team (ET) services (including environmental monitoring and audit (EM&A)) for the construction of M+ Museum Main Works (Contract No.: CC/2015/3A/022) and Lyric Theatre Complex including the Foundation Works (Contract No.: CC/2015/3A/014) and L1 Contract (Contract No. CC/2017/3A/030) at West Kowloon Cultural District (WKCD) (The Project) as part of the WKCD development. The Project Proponent is the West Kowloon Cultural District Authority (WKCDA). The construction works and EM&A programme for M+ Museum and Lyric Theatre Complex commenced on 31 October 2015 and 1 March 2016 respectively.
The overall works for the WKCD fall under two separate categories of Designated Project (DP) of the Environmental Impact Assessment Ordinance (EIAO), namely an “engineering feasibility study of urban development projects with a study area covering more than 20 ha or involving a total population of more than 100 000” (Item 3 of Schedule 3) and “an underpass more than 100m in length under the built areas” (Item A.9, Part I, Schedule 2). An Environmental Permit No. EP-453/2013/B (EP) was issued with respect to the “Underpass Road and Austin Road Flyover Serving the West Kowloon Cultural District” which specifically includes the abovementioned category of DP under Item A.9, Part I, Schedule 2 of the EIAO.
This Monthly EM&A Report presents the monitoring works at M+ Museum and Lyric Theatre Complex from 1 August to 31 August 2019.
Exceedance of Action and Limit Levels
There was no breach of Action or Limit levels for Air Quality (1-hour TSP and 24-hour TSP) and Noise in this reporting month.
Implementation of Mitigation Measures
Construction phase weekly site inspections were carried out 6, 13, 22 and 27 August 2019 for M+ Museum and 2, 7, 14, 21 and 28 August 2019 for Lyric Theatre Complex to confirm the implementation measures undertaken by the Contractors in the reporting month. The outcomes are presented in Section 4 and the status of implementation of mitigation measures in the site is shown in Appendix J.
Landscape and visual impact inspections were conducted as part of the abovementioned weekly site inspections during the reporting month. No adverse comment on landscape and visual aspects was made during these inspections.
EPD site inspection with contractor was conducted on 20 August 2019 at M+ Museum. No adverse comment was made and EPD kindly reminded the contractor to keep dust control for large stockpile at seaside.
EPD site inspections with contractor were conducted on 6, 20 and 30 August 2019 at Lyric Theatre Complex. No adverse comment was made and EPD friendly reminded the contractor to fully cover the stockpile as soon as possible and provide regular water spraying on site.
Record of Complaints
One environmental complaint was recorded in the reporting month.
Record of Notification of Summons and Successful Prosecutions
No notification of summons and successful prosecution were recorded in the reporting month.
Future Key Issues
The major site works for M+ Museum scheduled to be commissioned in the coming month include:
● Structure
– M+ Podium: Structural works completed
– CSF RT/F: Structural works completed
– RDE 15F: Structure work for Slab rebar & column preparation
● Facade
– Installation of panels on M+ tower completed
– Installation of façade on 8/F of RDE
● MEP
– BEL, ELV, BFS, BPD, BME works from B2 to 3/F of M+
– BEL, ELV, BFS, BPD, BME works from G/F to 15/F of RDE
– BEL, ELV, BFS, BPD, BME works from G/F to 11/F
● ABWF
– Block wall erection, Floor screed for plant room area and corridor area, wall plastering work up to M+ G/F – 3/F
– Blockwork plaster, paint/sealer, plaster, drywall subframe, Front of house work wall plastering work up to M+ 16/F
– Steel platform, Platering, Artwall/drywall stud erection, False ceiling sub-frame installation of RDE from 1MF to 5/F
– Fairface remedial work, gypsum block, waterproofing, flor screed, foamglas and gypsum block, skim coat and painting, self-levelling screed, floating floor of CSF building from 1/F to 8/F
The major site works for Lyric Theatre Complex scheduled to be commissioned in the coming month include:
● Excavation work at Main Cofferdam
● Drainage work (PIW works)
● Extended basement structure construction of Area 06 and Main Cofferdam
Potential environmental impacts due to the construction activities, including air quality, noise, water quality, waste, landscape and visual, will be monitored or reviewed. The recommended environmental mitigation measures shall be implemented on site and regular inspections as required will be carried out to ensure that the environmental conditions are acceptable.
Mott MacDonald Hong Kong Limited (MMHK) was commissioned to undertake the Environmental Team (ET) services (including environmental monitoring and audit (EM&A)) for the construction of M+ Museum Main Works (Contract No.: CC/2015/3A/022) and Lyric Theatre Complex including the Foundation Works (Contract No.: CC/2015/3A/014) and L1 Contract (Contract No. CC/2017/3A/030) at West Kowloon Cultural District (WKCD) (The Project) as part of the WKCD development. The Project Proponent is the West Kowloon Cultural District Authority (WKCDA). The construction works and EM&A programme for M+ Museum and Lyric Theatre Complex commenced on 31 October 2015 and 1 March 2016 respectively.
The overall works for the WKCD fall under two separate categories of Designated Project (DP) of the Environmental Impact Assessment Ordinance (EIAO), namely an “engineering feasibility study of urban development projects with a study area covering more than 20 ha or involving a total population of more than 100 000” (Item 3 of Schedule 3) and “an underpass more than 100m in length under the built areas” (Item A.9, Part I, Schedule 2). An Environmental Permit No. EP-453/2013/B (EP) was issued with respect to the “Underpass Road and Austin Road Flyover Serving the West Kowloon Cultural District” which specifically includes the abovementioned category of DP under Item A.9, Part I, Schedule 2 of the EIAO. The captioned projects include part of the abovementioned underpass road located within the site boundary also falls under this same category.
The M+ Museum development aims to provide an iconic presence for the M+ Museum, semi-transparent vertical plane, housing education facilities, a public restaurant and museum offices. At ground and lower levels, generous access will be provided to the park and other West Kowloon Cultural District facilities, alongside a public resource centre, theatres, retail and dining, and back-of-house functions.
The 1,200-seat Lyric Theatre Complex will be Hong Kong’s first world-class facility for dance performances, including ballet, contemporary and Chinese dance forms. In the run up to the opening of further major performing arts venues in the WKCD, it will also be used for a wide variety of performing arts events including drama, opera and musical performances. The Lyric Theatre Complex will act as a platform for Hong Kong’s leading arts organisations, and be a new major venue to show programmes from Asia and worldwide.
The Monthly EM&A Report is prepared in accordance with the Condition 3.4 of the Environmental Permit No. EP-453/2013/B. This Monthly EM&A Report presents the monitoring works at M+ Museum and Lyric Theatre Complex from 1 August to 31 August 2019. The purpose of this report is to summarise the findings in the EM&A of the project over the reporting period.
The organisation chart and lines of communication with respect to the on-site environmental management structure together with the contact information of the key personnel are shown in Appendix A.
During the reporting period, construction works at M+ Museum undertaken include:
● Structure
– M+ Podium: Structural works completed
– CSF RT/F: Structural works completed
– RDE 15F: Structure work for Slab rebar & column preparation
● Facade
– Installation of panels on M+ tower on East side
– Erection of 1MF scaffold for 1MF Installation
– Installation of façade on 7/F of RDE
● MEP
– BEL, ELV, BFS, BPD, BME works from B2 to 3/F of M+
– BEL, ELV, BFS, BPD, BME works from G/F to 15/F of RDE
– BEL, ELV, BFS, BPD, BME works from G/F to 11/F
● ABWF
– Block wall erection, Floor screed for plant room area and corridor area, wall plastering work up to M+ G/F – 3/F
– Blockwork plaster, paint/sealer, plaster, drywall subframe, Front of house work wall plastering work up to M+ 16/F
– Steel platform, Platering, Artwall/drywall stud erection, False ceiling sub-frame installation of RDE from 1MF to 5/F
– Fairface remedial work, gypsum block, waterproofing, flor screed, foamglas and gypsum block, skim coat and painting, self-levelling screed, floating floor of CSF building from 1/F to 8/F
During the reporting period, construction works at Lyric Theatre Complex undertaken include:
● Excavation and ELS works at Main Cofferdam
● Drainage and water mains work (PIW works)
● Extended basement structure construction of Area 6
The Construction Works Programme of M+ Museum and Lyric Theatre Complex is provided in Appendix B. A layout plan of the Project is provided in Figure 1. Please refer to Table 4.3 and Table 4.4 on the status of the environmental licenses.
The EM&A programme requires environmental monitoring of air quality, noise, landscape and visual as specified in the approved EM&A Manual.
A summary of impact EM&A requirements is presented in Table 1.1.
Table 1.1: Summary of Impact EM&A Requirements
Parameters |
Descriptions |
Locations |
Frequencies |
Air Quality |
24-Hour TSP |
AM1 - International Commerce Centre |
At least once every 6 days |
1-Hour TSP |
AM1 - International Commerce Centre |
At least 3 times every 6 days |
|
24-Hour TSP |
AM2B – Austin Road West opposite to The Harbourside Tower 1 |
At least once every 6 days |
|
1-Hour TSP |
AM2B – Austin Road West opposite to The Harbourside Tower 1 |
At least 3 times every 6 days |
|
Noise |
Leq, 30 minutes |
NM1A- Podium level of The Harbourside Tower 1 |
Weekly |
Landscape & Visual |
Monitor implementation of proposed mitigation measures during the construction stage |
As described in Table 9.1 and 9.2 of the EM&A Manual |
Bi-weekly |
Given that the Project covers only a small part of the whole WKCD area (i.e. M+ Museum, Lyric Theatre Complex and respective portions of underpass road), it was proposed that the EM&A programme for the Project should only require 1 noise monitoring station and 2 air quality monitoring stations located closest to the Project area. Currently, the works under the captioned project are confined in the western part of the WKCD site. Therefore, only the monitoring stations AM1, AM2 and NM1 were set up. Other monitoring locations are too far away (i.e. AM3 to AM5 and NM2 to NM5) are not included in this EM&A programme until the construction of the corresponding area commences.
The Harbourside management office formally rejected our proposal of setting up air quality and noise monitoring equipment on its premises at the podium level of Tower 1 (AM2/NM1) on 10 November 2015. Alternative noise monitoring location was identified at The Arch (NM2), however The Arch management office formally rejected our proposal of setting up noise monitoring equipment on its premises on 23 November 2015. Nevertheless, suitable air quality monitoring location at AM2 was identified on the ground floor in front of The Harbourside Tower 1, which is at the same location as that of baseline monitoring for consistency. No management approval is required at the ground floor for conducting the air monitoring. However, the electricity supply at AM2 was suspended from 31 August 2016 and was no longer available. In order to have a more secure electricity supply, an alternative air monitoring location (AM2A) was identified at Austin Road West opposite to The Harbourside Tower 1, which is close to Lyric Theatre Complex site entrance. This alternative air monitoring location was approved by EPD on 28 September 2016. Due to works programme, the air monitoring location AM2A has been relocated to the alternative monitoring location AM2B at the 1st floor of Gammon’s site office, which was approved by EPD on 21 February 2019. Meanwhile, the opportunity of setting up the air monitoring location at The Harbourside is being explored. Noise monitoring at G/F of Harbourside will not be representative. Approval from the management office of the International Commerce Centre has been granted on 29 February 2016 for conducting noise monitoring at the alternative noise monitoring location identified at the podium floor (NM1A) which is free from screening to the construction activities. Therefore, 2 air quality monitoring stations and 1 noise impact monitoring station were confirmed for the impact monitoring.
The Environmental Quality Performance Limits for air quality and noise are shown in Appendix C.
The Event and Action Plan for air quality, construction noise. landscape and visual are shown in Appendix D.
The EM&A programme followed the recommended mitigation measures in the EM&A Manual. The EM&A requirements as well as the summary of implementation status of the environmental mitigation measures are provided in Appendix J.
For air quality and noise, the monitoring methodology, including the monitoring locations, monitoring equipment used, monitoring parameters, and frequency and duration etc., for air quality and noise are detailed in this Section. The environmental monitoring schedules for the reporting period and the tentative monitoring Schedule for the coming month are provided in Appendix E.
For landscape and audit impact, the relevant EM&A monitoring requirements and details are also presented in this Section.
Table 2.1 summarizes the monitoring parameters, frequency and duration of the TSP monitoring.
Table 2.1: Air Quality Monitoring Parameters, Frequency and Duration
Parameter |
Frequency |
Duration |
24-hour TSP |
At least once in every six-days |
24 hours |
1-hour TSP |
At least 3 times every six-days |
60 minutes |
Currently, the works under the captioned project are confined in the western part of the WKCD site. Therefore, only the monitoring stations AM1 and AM2B were set up at the proposed locations in accordance with updated EM&A Manual. Location of the monitoring station is given in Table 2.2 and shown in Figure 1.
Table 2.2: Air Quality Monitoring Station
Monitoring Station |
Location |
AM1 |
International Commerce Centre (ICC) |
AM2B |
Austin Road West opposite to The Harbourside Tower 1 |
Continuous 24-hour TSP air quality monitoring was conducted using High Volume Sampler (HVS) (Model: TE-5170) located at the designated monitoring station. The HVS meets all the requirements stated in of the EM&A Manual. Portable direct reading dust meter was used to carry out the 1-hour TSP monitoring. Table 2.3 summarizes the equipment used in the impact air quality monitoring. Copies of the calibration certificates for the HVS, calibration kit and portable dust meters are attached in Appendix F.
Table 2.3: TSP Monitoring Equipment
Equipment |
Model |
24-hour TSP monitoring |
|
High Volume Sampler |
TE-5170 (Serial No.: 0767 and 8919) |
Calibrator |
TE-5025A (Orifice I.D.: 2454) |
1-hour TSP monitoring |
|
Portable direct reading dust meter |
Sibata LD-3B (Serial No.: 235780 and 6Z7784) |
Calibration of the HVS (five point calibration) using Calibration Kit was carried out every two months. The HVS calibration orifice will be calibrated annually. Calibration certificate of the TE-5025A Calibration Kit and the HVS are provided in Appendix F
The 1-hour TSP monitoring should be determined periodically (e.g. annually) by the HVS to check the validity and accuracy of the results measured by direct reading method.
24-hour TSP Monitoring
Installation
The HVS was installed at the site boundary. The following criteria were considered in the installation of the HVS.
– A horizontal platform with appropriate support to secure the sampler against gusty wind was provided.
– The distance between the HVS and any obstacles, such as buildings, was at least twice the height that the obstacle protrudes above the HVS.
– A minimum of 2 metres separation from walls, parapets and penthouse was required for rooftop sampler.
– A minimum of 2 metres separation from any supporting structure, measured horizontally was required.
– No furnace or incinerator flues or building vent were nearby.
– Airflow around the sampler was unrestricted.
– The sampler has been more than 20 metres from any drip line.
– Permission was obtained to set up the sampler and to obtain access to the monitoring station.
– A secured supply of electricity is needed to operate the sampler.
Preparation of Filter Papers
– Glass fibre filters were labelled and sufficient filters that were clean and without pinholes were selected.
– The filters used are specified to have a minimum collection efficiency of 99 percent for 0.3 µm (DOP) particles.
– All filters were equilibrated in the conditioning environment for 24 hours before weighing. The conditioning environment temperature was around 25 °C and not variable by more than ±3 °C with relative humidity (RH) < 50% and was not variable by more than ±5 %. A convenient working RH was 40%. All preparation of filters was done by Hong Kong Laboratory Accreditation Scheme (HOKLAS) accredited laboratory.
Field Monitoring Procedures
– The power supply was checked to ensure the HVS works properly.
– The filter holder and the area surrounding the filter were cleaned.
– The filter holder was removed by loosening the four bolts and a new filter, with stamped number upward, on a supporting screen was aligned carefully.
– The filter was properly aligned on the screen so that the gasket formed an airtight seal on the outer edges of the filter.
– The swing bolts were fastened to hold the filter holder down to the frame. The pressure applied should be sufficient to avoid air leakage at the edges.
– The shelter lid was closed and was secured with the aluminium strip.
– The HVS was warmed-up for about 5 minutes to establish run-temperature conditions.
– A new flow rate record sheet was set into the flow recorder.
– The flow rate of the HVS was checked and adjusted at around 1.3 m3/min. The range specified in the EM&A Manual was between 0.6-1.7 m3/min.
– The programmable timer was set for a sampling period of 24 hours, and the starting time, weather condition and the filter number were recorded.
– The initial elapsed time was recorded.
– At the end of sampling, the sampled filter was removed carefully and folded in half length so that only surfaces with collected particulate matter were in contact.
– It was then placed in a clean plastic envelope and sealed.
– All monitoring information was recorded on a standard data sheet.
– Filters were sent to a Hong Kong Laboratory Accreditation Scheme (HOKLAS) accredited laboratory for analysis.
Maintenance and Calibration
– The HVS and its accessories are maintained in good working condition, such as replacing motor brushes routinely and checking electrical wiring to ensure a continuous power supply.
– HVSs were calibrated upon installation and thereafter at bi-monthly intervals. The calibration kits were calibrated annually.
– Calibration records for HVS and calibration kit are shown in Appendix F.
1-hour TSP Monitoring
Field Monitoring
The measuring procedures of the 1-hour dust meter are in accordance with the Manufacturer’s Instruction Manual as follows:
– Turn the power on.
– Close the air collecting opening cover.
– Push the “TIME SETTING” switch to [BG].
– Push “START/STOP” switch to perform background measurement for 6 seconds.
– Turn the knob at SENSI ADJ position to insert the light scattering plate.
– Leave the equipment for 1 minute upon “SPAN CHECK” is indicated in the display.
– Push “START/STOP” switch to perform automatic sensitivity adjustment. This measurement takes 1 minute.
– Pull out the knob and return it to MEASURE position.
– Setting time period of 1 hour for the 1-hour TSP measurement.
– Push “START/STOP” to start the 1-hour TSP measurement.
– Regular checking of the time period setting to ensure monitoring time of 1 hour.
Maintenance and Calibration
– The 1-hour dust meter would be checked at 3-month intervals and calibrated at 1-year intervals throughout all stages of the air quality monitoring.
– Calibration records for direct dust meters are shown in Appendix F.
Weather Condition
– Meteorological data extracted from Hong Kong Observatory for the reporting month is provided in Appendix H.
Table 2.4 summarizes the monitoring parameters, frequency and duration of noise monitoring. The noise in A-weighted levels Leq, L10 and L90 are recorded in a 30-minute interval between 0700 and 1900 hours.
Table 2.4: Noise Monitoring Parameters, Period and Frequency
Time Period |
Parameters |
Frequency |
Daytime on normal weekdays (0700-1900 hours) |
Leq(30 min), L90(30 min) & L10 (30 min) |
Once every week |
Currently, the works under the captioned project are confined in the western part of the WKCD site. Therefore, only the monitoring station NM1A was set up at the proposed location in accordance with updated EM&A Manual. Location of the monitoring station is given in Table 2.5 and shown in Figure 1.
Table 2.5: Noise Monitoring Station
Monitoring Station |
Location |
NM1A |
Podium floor of International Commerce Centre (ICC) |
Integrating Sound Level Meter was used for noise monitoring. It was a Type 1 sound level meter capable of giving a continuous readout of the noise level readings including equivalent continuous sound pressure level (LAeq) and percentile sound pressure level (Lx). They comply with International Electrotechnical Commission Publications 651:1979 (Type 1) and 804:1985 (Type 1). Table 2.6 summarizes the noise monitoring equipment model being used.
Table 2.6: Noise Monitoring Equipments
Monitoring Station |
Equipment Model |
|
|
|
|
|
Integrating Sound Level Meter |
Calibrator |
Rion NL-52 (Serial No. 00542913) |
LARSON DAVIS CAL200 (Serial No. 15678) |
Field Monitoring
– The microphone of the Sound Level Meter was set at least 1.2 m above the ground.
– Free Field measurement was made at the monitoring locations.
– The battery condition was checked to ensure the correct functioning of the meter.
– Parameters such as frequency weighting, the time weighting and the measurement time were set as follows:
- frequency weighting: A
- time weighting: Fast
- time measurement: 30 minutes intervals (between 0700-1900 on normal weekdays)
– Prior to and after each noise measurement, the meter was calibrated using a Calibrator for 94 dB at 1 kHz. If the difference in the calibration level before and after measurement was more than 1 dB, the measurement would be considered invalid and has to be repeated after re-calibration or repair of the equipment.
– During the monitoring period, the Leq, L10 and L90 were recorded. In addition, any site observations and noise sources were recorded on a standard record sheet.
– A correction of +3dB(A) was made to the free field measurements.
Maintenance and Calibration
– The microphone head of the sound level meter and calibrator is cleaned with soft cloth at quarterly intervals.
– The sound level meter and calibrator are sent to the supplier or HOKLAS laboratory to check and calibrate at yearly intervals.
– Calibration records are shown in Appendix F.
Weather Condition
– Meteorological data extracted from Hong Kong Observatory for the reporting month is provided in Appendix H.
Table 2.7 details the monitoring program (as proposed in the WKCD EIA report) for landscape and visual impact during the construction phase.
Table 2.7: Monitoring Program for Landscape and Visual Impact during Construction Phase
Stage |
Monitoring Task |
Frequency |
Report |
Approval |
Construction |
Monitor implementation of proposed mitigation measures during the construction stage. |
Bi-weekly |
ET to report on Contractor’s compliance |
Counter-signed by IEC |
During the landscape and visual impact monitoring, any changes in relation to the landscape and visual amenity should be monitored with reference to the baseline conditions of the site. In addition, mitigation measures were proposed in the WKCD EIA report to minimise the landscape and visual impacts during the construction phase. The proposed mitigation measures as shown in Table 9.1 and Table 9.2 of the EM&A Manual should be checked for proper implementation.
Construction impact monitoring for air quality, noise and landscape and visual impact was undertaken in compliance with the EM&A Manual during the reporting month.
Results of 1-hour TSP at the monitoring location AM1 and AM2B are summarised in Table 3.1. Graphical plots of the monitoring results are shown in Appendix G.
Table 3.1: Summary of 1-hour TSP monitoring results
Monitoring Station |
Monitoring Date |
Start Time |
1-hour TSP (μg/m3) |
Range (μg/m3) |
Action Level (μg/m3) |
Limit Level (μg/m3) |
||
|
|
|
||||||
|
|
|
1st Result |
2nd Result |
3rd Result |
|
|
|
AM1 |
01-Aug-19 |
08:12 |
65 |
72 |
80 |
28 – 83 |
273.7 |
500 |
07-Aug-19 |
08:18 |
31 |
42 |
49 |
||||
13-Aug-19 |
13:19 |
31 |
28 |
35 |
||||
19-Aug-19 |
08:20 |
67 |
75 |
83 |
||||
23-Aug-19 |
13:23 |
34 |
37 |
35 |
||||
29-Aug-19 |
13:20 |
32 |
39 |
35 |
||||
AM2B |
01-Aug-19 |
08:27 |
67 |
73 |
81 |
39 – 85 |
274.2 |
500 |
07-Aug-19 |
08:32 |
66 |
59 |
64 |
||||
13-Aug-19 |
13:28 |
40 |
39 |
51 |
||||
19-Aug-19 |
08:36 |
69 |
77 |
85 |
||||
23-Aug-19 |
13:39 |
64 |
58 |
55 |
||||
29-Aug-19 |
13:34 |
49 |
52 |
48 |
Results of 24-hour TSP at the monitoring location AM1 and AM2B are summarised in Table 3.2. Graphical plots of the monitoring results are shown in Appendix G.
Table 3.2: Summary of 24-hour TSP monitoring results
Monitoring Station |
Monitoring Date |
Start Time |
Monitoring Results (μg/m3) |
Range (μg/m3) |
Action Level (μg/m3) |
Limit Level (μg/m3) |
AM1 |
01-Aug-19 |
08:10 |
23 |
18 – 42 |
143.6 |
260 |
07-Aug-19 |
08:15 |
20 |
||||
13-Aug-19 |
08:15 |
18 |
||||
19-Aug-19 |
08:18 |
42 |
||||
23-Aug-19 |
08:20 |
28 |
||||
29-Aug-19 |
08:18 |
27 |
||||
AM2B |
01-Aug-19 |
08:25 |
31 |
27 – 52 |
151.1 |
260 |
07-Aug-19 |
08:30 |
41 |
||||
13-Aug-19 |
08:26 |
27 |
||||
19-Aug-19 |
08:34 |
52 |
||||
23-Aug-19 |
08:36 |
41 |
||||
29-Aug-19 |
08:32 |
40 |
No exceedance of 1-hour and 24-hour TSP (Action or Limit Level) was recorded in the reporting period.
The construction noise monitoring results at the monitoring location NM1A are summarized in Table 3.3. Graphical plots of the monitoring data and the station set-up of a free-field measurement are shown in Appendix G.
Table 3.3: Summary of noise monitoring results during normal weekdays
Monitoring Date |
Start Time |
End Time |
Leq (30 mins)*, dB(A) |
Limit Level for Leq (dB(A)) |
01-Aug-19 |
10:50 |
11:20 |
68.9 |
75 |
07-Aug-19 |
10:38 |
11:08 |
68.9 |
|
13-Aug-19 |
10:17 |
10:47 |
69.4 |
|
19-Aug-19 |
10:46 |
11:16 |
68.5 |
|
29-Aug-19 |
10:43 |
11:13 |
69.1 |
Remarks: * +3dB (A) correction was applied to free-field measurement. |
No exceedance (Action/Limit Level) of construction noise was recorded in the reporting period as no noise related environmental complaint was received during the reporting period and noise levels recorded during the monitoring period were below 75 dB(A).
Landscape and visual impact inspections were conducted as part of the weekly site inspections on 6 and 22 August 2019 for M+ Museum, and 2, 14 and 28 August 2019 for Lyric Theatre Complex during the reporting month. As reviewed by the registered Landscape Architect, no adverse comment on landscape and visual aspects was made during these inspections.
The landscape and visual mitigation measures were implemented during the reporting period. The summary of implementation status of the environmental mitigation measures is provided in Appendix J.
Construction phase weekly site inspections were carried out on 6, 13, 22 and 27 August 2019. The joint site inspection with IEC, ET, ER and Contractor was held on 13 August 2019. All observations have been recorded in the site inspection checklist and passed to the Contractor together with the appropriate recommended mitigation measures where necessary.
EPD site inspection with contractor was conducted on 20 August 2019. EPD had inspected wastewater treatment facilities, emergency generator at ICP and discharge point at DCS. Regular water samplings were taken on wastewater treatment facilities and sea water cooled chilled water system. No adverse comment was made and EPD kindly reminded the contractor to keep dust control for large stockpile at seaside.
The key observations from the site inspections and associated recommendations are summarized in Table 4.1.
Table 4.1: Summary of Site Inspections and Recommendations for M+ Museum
Inspection Date |
Parameter |
Observation / Recommendation |
Contactor’s Responses / Action(s) Undertaken |
Close-out (Date) |
6 Aug 2019 |
Water quality |
Effluent quality of wetsep was checked. It was found visually clear when comparing with standard solution and within proper pH range. |
N/A |
N/A |
13 Aug 2019 |
Water quality |
Effluent quality of wetsep was checked. It was found visually clear when comparing with standard solution and within proper pH range. |
N/A |
N/A |
13 Aug 2019 |
Air Quality |
Stockpile and haul road were observed without cover and dusty. The contractor was reminded to cover the stockpile with impervious sheeting and spray water during operation. |
The contractor has covered the stockpile with impervious sheeting and spray the haul road to avoid dust impact. |
14 Aug 2019 |
22 Aug 2019 |
Water quality |
Effluent quality of wetsep was checked. It was found visually clear when comparing with standard solution and within proper pH range. |
N/A |
N/A |
27 Aug 2019 |
Water quality |
Effluent quality of wetsep was checked. It was found visually clear when comparing with standard solution and within proper pH range. |
N/A |
N/A |
Construction phase weekly site inspections were carried out on 2, 7, 14, 21 and 28 August 2019. The joint site inspection with IEC, ET, ER and Contractor was held on 21 August 2019. All observations have been recorded in the site inspection checklist and passed to the Contractor together with the appropriate recommended mitigation measures where necessary.
EPD site inspections with contractor were conducted on 6, 20 and 30 August 2019. EPD had inspected the wastewater treatment facilities, dewatering / drainage system at the main cofferdam, bunding at the seafront, outfall of the box culvert, PIW site area, discharge point of WWTP at car park, and seawall area. No adverse comment was made and EPD friendly reminded the contractor to fully cover the stockpile as soon as possible and provide regular water spraying on site.
The key observations from the site inspections and associated recommendations are summarized in Table 4.2.
Table 4.2: Summary of Site Inspections and Recommendations for Lyric Theatre Complex
Inspection Date |
Parameter |
Observation / Recommendation |
Contactor’s Responses / Action(s) Undertaken |
Close-out (Date) |
7 Aug 2019 |
Waste Management |
No drip tray was observed for chemicals. The contractor was reminded to provide suitable drip tray for those chemicals. |
Chemicals were relocated at a suitable place |
14 Aug 2019 |
14 Aug 2019 |
Water Quality |
Meter of wetsep was wrongly display the pH value. The contractor was reminded to repair the meter in order to display a correct pH value. |
The contractor has repaired the meter and kept the pH value within the acceptable range (6-9). |
19 Aug 2019 |
21 Aug 2019 |
Water Quality |
A blue pipe was observed at the water discharge point connecting from other construction sites. The contractor was reminded to review the discharge point condition. |
The contractor has removed the blue pipe at the water discharge point and kept it in good condition. |
22 Aug 2019 |
28 Aug 2019 |
Air Quality |
The grouting station was observed without fully cover. The contractor was reminded to fully cover with three sides and tops. |
The contractor has fully covered the grouting station with three sides and tops. |
31 Aug 2019 |
28 Aug 2019 |
Waste Management |
The contractor was reminded to provide suitable drip tray for the wetsep chemicals. |
The contractor has provided suitable drip tray for the wetsep chemicals. |
31 Aug 2019 |
The Contractors have been registered as a chemical waste producer for the Project. Construction and demolition (C&D) material sorting will be carried out on site. A sufficient number of receptacles were available for general refuse collection.
As advised by the Contractor, 0 tonnes, 136.6 tonnes and 217.49 tonnes of inert C&D material were disposed of as public fill to Chai Wan Public Fill Barging Point, Tuen Mun Area 38 Public Fill and Tseung Kwan O Area 137 Public Fill respectively, while 596.8 tonnes of general refuse were disposed of at SENT landfill. 1.5 tonnes of metals, 0 tonne of paper/cardboard packaging, 0 tonne of plastic and 0 tonnes of timber were collected by recycling contractors in the reporting month. 0 tonne of inert C&D materials was reused on site. 0 tonnes of inert C&D materials were reused in other projects and 283.3 tonnes of inert C&D materials were disposed to sorting facility. 0 tonne of chemical waste was collected by licensed contractors in the reporting period.
The cumulative waste generation records for M+ Museum are shown in Appendix I.
As advised by the Contractor, 2,068.17 tonnes and 416.88 tonnes of inert C&D material were disposed of as public fill to Tseung Kwan O Area 137 and Tuen Mun Area 38 Public Fill, while 66.3 tonnes of general refuse were disposed of at SENT and WENT landfill. 40.2 tonnes of metals, 0 tonne of paper/cardboard packaging, 0 tonne of plastic and 0 tonne of timber was collected by recycling contractors in the reporting month. 0 tonne of inert C&D materials was reused on site. 0 tonnes of inert C&D materials were reused in other projects and 31.9 tonnes of inert C&D materials were imported for reuse at site. 27.8 tonnes of inert C&D materials were disposed to sorting facility and 0 tonne of chemical waste was collected by licensed contractors in the reporting period.
The actual amounts of different types of waste generated by the activities of construction works at Lyric Theatre Complex in the reporting month are shown in Appendix I.
The environmental permits, licenses, and/or notifications on environmental protection for this Project which were valid during the period are summarised in Tables 4.3 and 4.4.
Table 4.3: Status of Environmental Submissions, Licenses and Permits for M+ Museum
Permit / License No. / Notification / Reference No. |
Valid Period |
Status |
Remarks |
|
|
|
|||
|
From |
To |
|
|
Chemical Waste Producer Registration |
||||
WPN5213-217-G2347-53 |
04-Oct-18 |
-- |
Valid |
-- |
Billing Account Construction Waste Disposal |
||||
7031993 |
03-Oct-18 |
-- |
Account Active |
-- |
Construction Noise Permit |
||||
GW-RE0461-19 |
18-Jun-19 |
12-Dec-19 |
Cancelled |
-- |
GW-RE0669-19 |
28-Aug-19 |
26-Feb-20 |
Valid |
This new construction noise permit was applied to replace the existing permit |
Wastewater Discharge License |
||||
WT-00033363-2019 |
21-Mar-19 |
31-Mar-24 |
Valid |
-- |
Notification under Air Pollution Control (Construction Dust) Regulation |
||||
437339 |
12-Sep-18 |
-- |
Notified |
-- |
Table 4.4: Status of Environmental Submissions, Licenses and Permits for Lyric Theatre Complex
Permit / License No. / Notification / Reference No. |
Valid Period |
Status |
Remarks |
|
|
|
|||
|
From |
To |
|
|
Chemical Waste Producer Registration |
||||
WPN5213-217-G2347-39 |
17-Feb-16 |
-- |
Valid |
-- |
Billing Account Construction Waste Disposal |
||||
7029925 |
22-Jan-18 |
-- |
Account Active |
-- |
Construction Noise Permit |
||||
GW-RE0483-19 |
21-Jun-19 |
16-Dec-19 |
Valid |
-- |
Wastewater Discharge License |
||||
WT-00030694-2018 |
6-Apr-18 |
30-Apr-23 |
Valid |
-- |
Notification under Air Pollution Control (Construction Dust) Regulation |
||||
429708 |
16-Jan-18 |
-- |
Notified |
-- |
The EM&A programme followed the recommended mitigation measures in the EM&A Manual. The EM&A requirements as well as the summary of implementation status of the environmental mitigation measures are provided in Appendix J. In particular, the following mitigation measures were brought to attention during the site inspections:
– Dusty materials should be covered entirely by imperious sheeting to prevent emission of fugitive dust.
– Haul road should be sprayed with water during operation.
– The grouting station should be fully covered with three sides and tops.
Water Quality
– The pH meter should be repaired in order to display a correct pH value.
– The discharge point condition should be reviewed to ensure that all discharge comes from the site only.
Waste Management
– Suitable drip tray should be provided for chemicals.
The status of the required submission under the EP during the reporting period is summarized in Table 5.1.
Table 5.1: Status of Submissions under the Environmental Permit
EP Condition |
Submission |
Submission Date |
Condition 3.4 |
Monthly EM&A Report for July 2019 |
14 August 2019 |
There was no breach of Action or Limit Levels for Air Quality and Noise monitoring in the reporting month.
One environmental complaint was received in the reporting month.
Referred an email from EPD dated 5 August 2019, a complaint was received from the resident of the Victoria Towers about muddy water was discharged to the Victoria Harbour from the Lyric Theatre Complex.
After the investigation, the complaint was found to be non-project related. The muddy water discharged to the harbour was unlikely to be from the works of the Lyric Theatre Complex. Moreover, it should be noted that beside the Lyric Theatre Complex construction work, there were other construction works carried out by other contractors which may also contributed to the muddy water discharge. However, the contractor will continue implement on-site water quality mitigation measures to ensure the water discharge complies with the standards as stipulated in the discharge licence. The “Investigation Report for Complaint of Muddy Water Generated from the WKCDA Construction Site” was submitted to EPD on 26 August 2019.
On 28 August 2019, an email was received from EPD again regarding a site photo (taken approximate at 6 pm on 3 August 2019) from a complainant showing muddy water was discharged at seafront near WKCD Lyric Theatre site. Therefore, EPD would like to further investigate the complaint and provide additional information in the further investigation report for the complaint dated 5 August 2019.
After further investigation, no evidence was shown the muddy water discharged to the harbour was related to Lyric Theatre Complex. Also, it should be noted that besides the construction work at Lyric Theatre Complex, there were other construction works carried out by other contractors which may also contribute to the muddy water discharge. Nevertheless, the contractor was reminded to closely monitoring the situation and the water discharge quality.
The cumulative statistics on complaints were provided in Appendix K.
No notifications of summons or successful prosecution were received this month. The cumulative statistics on notifications of summons and successful prosecutions were provided in Appendix K.
The major site works for M+ Museum scheduled to be commissioned in the coming month include:
● Structure
– M+ Podium: Structural works completed
– CSF RT/F: Structural works completed
– RDE 15F: Structure work for Slab rebar & column preparation
● Facade
– Installation of panels on M+ tower completed
– Installation of façade on 8/F of RDE
● MEP
– BEL, ELV, BFS, BPD, BME works from B2 to 3/F of M+
– BEL, ELV, BFS, BPD, BME works from G/F to 15/F of RDE,
– BEL, ELV, BFS, BPD, BME works from G/F to 11/F
● ABWF
– Block wall erection, Floor screed for plant room area and corridor area, wall plastering work up to M+ G/F – 3/F
– Blockwork plaster, paint/sealer, plaster, drywall subframe, Front of house work wall plastering work up to M+ 16/F
– Steel platform, Platering, Artwall/drywall stud erection, False ceiling sub-frame installation of RDE from 1MF to 5/F
– Fairface remedial work, gypsum block, waterproofing, flor screed, foamglas and gypsum block, skim coat and painting, self-levelling screed, floating floor of CSF building from 1/F to 8/F
The major site works for Lyric Theatre Complex scheduled to be commissioned in the coming month include:
● Excavation work at Main Cofferdam
● Drainage work (PIW works)
● Extended basement structure construction of Area 06 and Main Cofferdam
Key issues to be considered in the coming month include:
● Generation of dust from construction works;
● Noise impact from operating equipment and machinery on-site;
● Generation of site surface runoffs and wastewater from activities on-site;
● Management of stockpiles and slopes, particularly on rainy days;
● Sorting, recycling, storage and disposal of general refuse and construction waste; and
● Management of chemicals and avoidance of oil spillage on-site.
Key issues to be considered in the coming month include:
● Generation of dust from construction works;
● Noise impact from operating equipment and machinery on-site;
● Generation of site surface runoffs and wastewater from activities on-site;
● Management of stockpiles and slopes, particularly on rainy days;
● Sorting, recycling, storage and disposal of general refuse and construction waste; and
● Management of chemicals and avoidance of oil spillage on-site.
The environmental site inspection and environmental monitoring will be continued in the coming month. Impact monitoring for air quality and noise in accordance with the approved EM&A Manual has commenced since 31 October 2015 and 5 March 2016 respectively. The tentative monitoring schedule for the coming month is shown in the Appendix E.
The EM&A programme as recommended in the EM&A Manual has been undertaken since the construction of M+ Museum main works commenced on 31 October 2015, and the construction of Lyric Theatre Complex commenced on 1 March 2016.
Monitoring of air quality and noise with respect to the Projects is underway. In particular, the 1-hour TSP, 24-hour TSP, noise level (as Leq, 30 minutes) under monitoring have been checked against established Action and Limit levels. There was no breach of Action and Limit Levels for 1-hour TSP, 24-hour TSP and noise in the reporting month.
One environmental complaint was recorded in the reporting month. No notifications of summons or successful prosecution were received during the reporting month.
Weekly construction phase site inspections and bi-weekly landscape and visual impact inspections were conducted during the reporting month as required. It was observed that the Contractors had implemented all possible and feasible mitigation measures to mitigate the potential environmental impacts during construction phase works.
Potential environmental impacts due to the construction activities, including air quality, noise, water quality, waste, landscape and visual, will be monitored or reviewed. The recommended environmental mitigation measures shall be implemented on site and regular inspections as required will be carried out to ensure that the environmental conditions are acceptable.