Issue No. : 1
Issue Date : February 2009
Project No. : 768
Joint User Complex and Wholesale Fish Market at Area 44, Tuen Mun
Environmental Monitoring & Audit Report
(January 2009)
Prepared By:
Allied Environmental Consultants Ltd.
COMMERCIAL-IN-CONFIDENCE
Issue No. : 1
Issue Date : February 2009
Project No. : 768
Joint User Complex and Wholesale Fish Market at Area 44, Tuen Mun
Environmental Monitoring & Audit Report (January 2009)
Prepared By:
Allied Environmental Consultants Ltd.
COMMERCIAL-IN-CONFIDENCE
Author:
Nic Lam
BSc(Hons)
Checked and Approved:
Grace Kwok
BEng(Hons) MHKIEIA MHKIOA
MISWA MIAIA MRAPA LEED AP
This report has been prepared by Allied Environmental Consultants Limited with all reasonable skill, care and diligence within the terms of the Agreement with the client, incorporating our General Terms and Conditions of Business and taking account of the resources devoted to it by agreement with the client.
We disclaim any responsibility to the client and others in respect of any matters outside the scope of the above.
This report is confidential to the client and we accept no responsibility of whatsoever nature to third parties to whom this report, or any part thereof, is made known. Any such party relies upon the report at their own risk.
Table of Contents
Table of Contents 1
List of Tables 2
List of Figures 2
List of Appendices 2
EXECUTIVE SUMMARY 3
1. PROJECT BACKGROUND 4
1.1 Project Organization and Contact Personnel 4
2. SENSITIVE RECEIVERS 5
3. CONSTRUCTION WORKS & PROGRAMME 5
4. SUMMARY OF EM&A REQUIREMENT 5
5. MONITORING METHODOLOGY 7
5.1 Monitoring Programme 7
5.2 Air Quality Monitoring 8
5.3 Noise Monitoring 8
6. RESULTS 8
6.1. Air Quality 8
6.2. Noise 9
6.3. Weather Conditions 10
7. SITE INSPECTION & AUDIT 10
8. Non-compliance, Complaints, Notifications of Summons and Successful Prosecutions 11
9. OTHERS 11
10. CONCLUSIONS 11
Table 1 Contact Details of Key Personnel
Table 2 Interrelationship between Construction Activities and Mitigation Measures
Table 3 Action and Limit Level for Air Quality Impact Monitoring at Yuet Wu Villa
Table 4 Action and Limit Levels for Construction Noise Impact Monitoring
Table 5 Event Action Plan
Table 6 Noise Monitoring Equipment
Table 7 1-hour TSP Monitoring Results
Table 8 24-hour TSP Monitoring Results
Table 9 Noise Monitoring Results
Table 10 Summary of Weather Conditions during the Monitoring Period
Table 11 Summary of Site Inspections
Figure 1 Site Location Plan
Figure 2 Location of Air Quality Monitoring Station
Figure 3 Location of Noise Monitoring Station
Figure 4 Photos of Air Quality Monitoring Station
Figure 5 Photos of Noise Monitoring Station
Figure 6 Photos of the Construction Site for the Junior Police Officers’ Married Quarters
Appendix A Calibration Record of High-Volume TSP Sampler
Appendix B Calibration Certification of the Sound Level Meter and Calibrator
Appendix C Summary of 1-Hour TSP Monitoring Record
Appendix D Summary of 24-Hour TSP Monitoring Record
Appendix E Summary of Noise Monitoring Record
Appendix F Wind Record from Hong Kong Observatory
Appendix G Mitigation Measures Implementation Schedule for Construction Stage
Allied Environmental Consultants Limited (AEC) has been appointed to conduct an environmental monitoring and audit (EM&A) program for the proposed Joint User Complex and Wholesale Fish Market at Area 44, Tuen Mun. The construction works were commenced on 31st July 2008. This report is the sixth monthly EM&A report, which detailed the environmental monitoring and audit results recorded during the period from 1st January 2009 to 31th January 2009.
Impact environmental monitoring for the proposed Joint User Complex and Wholesale Fish Market at Area 44, Tuen Mun has been carried out on 3rd, 9th, 15th, 21st and 29th January 2009 at Block 15, Yuet Wu Villa. 1-hr TSP and noise monitoring were conducted within the period of 0700-1900 hours, where 24-hr TSP monitoring was conducted continuously for a 24-hour period.
1-hour TSP monitoring results at the monitoring location ranged from 105μg/m3 to 189μg/m3 with an average of 155μg/m3. 24-hour TSP monitoring results ranged from 70μg/m3 to 87μg/m3 with an average of 79μg/m3.
Noise monitoring results at the monitoring location ranged from 60.2dB(A) to 62.2dB(A) with an average of 61.2dB(A).
Based on the monitoring results, the air quality and construction noise level complied with the environmental requirements in EM&A Manual. There were no breaches of the action and limit levels. There were no environmental complaints received in the reporting month. No notification of summons or prosecution was received.
Constructions activities will be undertaken in February 2009 include underground foundation works and drainage diversion. Potential environmental impacts include dust generation from stockpiles of dusty materials and the drainage diversion work; noise from operation of the equipments and jack piling, runoff from drainage diversion works and the storage of various C&D and chemical wastes. The Contractor should properly implement the required environmental mitigation measures as per the implementation schedule in the EM&A manual to ensure no significant adverse environmental impacts to be arisen from the construction works. The Contractor was reminded to maintain good housekeeping throughout the construction phase.
A Joint User Complex and Wholesale Fish Market (WFM Complex) at Area 44 in Tuen Mun is proposed to be designed and built by Architectural Services Department on behalf of Agriculture, Fisheries and Conservation Department, Marine Department, Home Affairs Department, and Food and Environmental Hygiene Department of the Hong Kong SAR. The WFM Complex is to provide a permanent site for the relocation of the existing temporary wholesale fish market at Tuen Mun Area 27 and to accommodate a community hall, a dragon boat racing spectator stand, and other community facilities for public use. The proposed development is a 3-storey complex to accommodate a wholesale fish market, a public toilet, a refuse collection point and a marine refuse collection point at the ground floor, a community hall on the first floor, and a dragon boat race spectator stand with landscaped deck on roof level. The proposed Wholesale Fish Market is categorized as a designated project under the Environmental Impact Assessment Ordinance (EIAO) and therefore a detailed Environmental Impact Assessment (EIA-085/2002) has been conducted in year 2002 and an Environmental Permit (EP-296/2007) was issued by Environmental Protection Department in December 2007.
The subject site is located at Castle Peak Bay of Tuen Mun given in Figure 1. The subject site is bounded to the north by a future local open space presently used as a temporary car park, to the east by Castle Peak Bay typhoon shelter, to the south by a future lorry park and to the west by Wu Shan Road. Yuet Wu Villa being the nearest residential establishment is located at around 85m from the site boundary.
Key personnel and contact particulars are summarized in Table 1.
Table 1 Contact Details of Key Personnel
Role |
Department / Company |
Names |
Contact Number |
Fax Number |
Lead User Department |
Agriculture, Fisheries, and Conservation Department |
Mr. K.H. Chan Ms. Louise Li |
2150 7092 2150 7140 |
2314 2866
|
Environmental Permit Holder |
Architecture Services Department |
Mr. S.W. Chow Ms. Susana Chan |
2867 3716 2867 6706 |
2523 9622
|
Architect |
P&T Architects and Engineers Ltd. |
Ms. Sarah Ng Ms. Vivian Law |
2835 3548 2832 3046 |
2891 3834
|
Main Contractor |
W. Hing Construction Co. Ltd. |
Mr. Andy Chan Mr. Tim Wong |
9630 7404 6478 4623 |
8343 9188 |
Environmental Team Leader |
Allied Environmental Consultants Ltd. |
Ms. Grace Kwok |
2815 7028 |
2815 5399 |
Independent Environmental Checker |
Cinotech Consultants Ltd. |
Mr. Alex Ngai |
2151 2083 |
3107 1388 |
Air Sensitive Receivers (ASRs) within 500m include Yuet Wu Villa, lawn bowling field, tennis court, which are less than 100m away from the subject site. Tuen Mun Wu Hong Clinic is located to the west at about 100m to the site boundary. Two secondary schools, Ka Chi Secondary School and South Tuen Mun Government Secondary School, are approximately 300m to the south of the site boundary.
Noise Sensitive Receivers (NSRs) within 300m are Yuet Wu Villa, Siu Hei Court, Yan Chai Hospital Low Chan Chor Si Primary School and Wu King Estate. The nearest NSR will be Block 15 of Yuet Wu Villa.
The major works undertaken and/or completed during the monitoring period are listed below:
- Underground foundation works
- Drainage diversion works
Table 2 shows the interrelationship between construction activities and environmental mitigation measures for the reporting month.
Table 2 Interrelationship between Construction Activities and Mitigation Measures
Construction Works |
Major Environmental Impact |
Mitigation Measures |
Underground foundation works |
Noise impact |
Well-maintained plants were used |
Drainage diversion |
Air quality, and water quality impacts |
Water spraying, avoided rainy days |
For regular impact monitoring, the sampling frequency of at least once in every six-days, shall be strictly observed at the monitoring station for 24-hr TSP monitoring. For 1-hr TSP monitoring, the sampling frequency of at least three times in every six-days should be undertaken when the highest dust impact occurs. For noise monitoring, one set of measurement between 0700-1900 hours on normal weekdays. Leq(30 min) shall be used as the monitoring parameter.
From baseline monitoring results, the proposed Action and Limit Levels for air quality are summarized in Table 3. The average baseline 1-hr TSP value of 129μg/m3 and 24-hr TSP value of 65μg/m3 measured at Block 15, Yuet Wu Villa was used to determine the action and limit level for air quality impact monitoring. The proposed Action and Limit Levels for construction noise are summarized in Table 4.
Table 3 Action and Limit Level for Air Quality Impact Monitoring at Yuet Wu Villa
Parameters |
Baseline Level (μg/m3) |
Action Level (μg/m3) |
Limit Level (μg/m3) |
24-Hour TSP Level |
65 |
173 |
260 |
1-Hour TSP Level |
129 |
334 |
500 |
Table 4 Action and Limit Levels for Construction Noise Impact Monitoring
Time Period |
Action Level |
Limit Level |
Daytime (0700-1900 hours) on weekdays |
When one documented compliant is received |
Dwelling 75dB(A)1 School 70dB(A)1 (65dB(A) during examinations)1 |
1900-2300 on any day and 0700-2300 on Sunday and general holidays, for use of PME2 |
When one documented compliant is received |
65dB(A)3 |
All days during the night-time (2300-0700 hours) 2 |
When one documented compliant is received |
50dB(A)3 |
Note: 1. Construction noise criteria stipulated in the TM-EIAO
2. A Construction Noise Permit (CNP) shall be required for the carrying out of the construction work during the restricted hours (1900-2300 on any day and 0700-2300 on Sunday and general holidays, for use of PME; and All days during the night-time (2300-0700 hours))
3. Area sensitivity rating of the monitoring location is “B”.
Should non-compliance of the above Action and Limit levels occurs, the contractor shall undertake corresponding in accordance with the proposed Event Action Plan given in the EM&A Manual. A summarized general Event Action Plan is given in Table 5. Details should be referred to the Event Action Plan in the EM&A Manual.
Level |
Step 1 |
Step 2 |
Step 3 |
Action |
l Identify source l Check monitoring data and working methods |
l Contact project manager to discuss and implement remedial action l Rectify any unacceptable practice l Amend working methods if appropriate l If exceedance continues, commence additional monitoring |
l Notify client/project manager following correct of the situation l Cease additional monitoring if exceedance stops |
Limit |
l Identify source l Notify client/project manager l Check monitoring data and working methods l Repeat measurement to confirm finding l Commence additional monitoring |
l Take immediate action to avoid further exceedance l Submit proposal for remedial actions to client/project manager within 3 working days l Implement the agreed proposal l If exceedance continues, amend and resubmit the proposal |
l Notify client/project manager following correction of the situation l Cease additional monitoring if exceedance stops |
Air quality monitoring and noise monitoring were conducted at Block 15, Yuet Wu Villa on 3rd, 9th, 15th, 21st and 29th January 2009. Air quality monitoring station was set up at the roof top of the residential block and noise monitoring was conducted at 1.2m above ground level at the junction of Wu Sau Street and Wu On Street as given in Figure 2 and 3. Figure 4 and 5 show photos taken during monitoring at the two locations.
A construction site for the proposed Junior Police Officers' Married Quarters is located at Wu Hong Street which is 110m away from the monitoring location, which can be a major source of the noise and TSP generation during the monitoring period. Figure 6 shows the photo of the construction site.
1-hour and 24-hour TSP air quality monitoring was conducted at the designated air quality monitoring location using a High Volume TSP Sampler (Model No: Anderson GMWS-2310 ACCU-VOL) at the designated location. The Calibration Record of the High-Volume TSP Sampler is given in Appendix A. 24-hour TSP samples were taken every six days. 1-hour TSP samples were taken three times a day between 0700-1900 hours.
Noise monitoring was conducted at the designated noise monitoring location between 0700-1900 hours using a sound level meter which complies with the International Electrotechnical Commission Publications 651:1979 (Type 1) and 804:1985 (Type 1). Noise instrumentation details are given in Table 6 and the Calibration Certificate for the sound level meter and calibrator is given in Appendix B.
Table 6 Noise Monitoring Equipment
Manufacturer |
Type/Model No. |
Equipment |
RION |
Model NL 31 |
Precision Sound Level Analyser with windshield |
RION |
Model NC 73 |
Calibrator |
Noise levels measurements were recorded in terms of thirty minutes A-weighted equivalent continuous sound pressure level (Leq(30min)) on a daily basis. The sound level meter was calibrated immediately prior to and following each noise measurement. The meter was mounted on a tripod at a height of 1.2m and the microphone was positioned at 1m away the building façade of the noise monitoring station facing the construction site.
Noise measurements were not made in the presence of fog, rain, and wind with a steady speed exceeding 5m/s or wind with gusts exceeding 10m/s. The wind speed was checked with a portable anemometer capable of measuring the wind speed in m/s.
1-hour and 24-hour TSP monitoring results are summarized in Table 7 and 8 and serve as the basis for determining the action and limit levels. The minimum and maximum 1-hour TSP measured at Yuet Wu Villa was 105μg/m3 and 189μg/m3 respectively with an average of 155μg/m3. The minimum and maximum 24-hour TSP measured was 70μg/m3 and 87μg/m3 respectively with an average of 79μg/m3. Summary of air quality monitoring record is provided in Appendix C and D.
Table 7 1-Hour TSP Monitoring Results
Day |
Date |
1-hr TSP (μg/m3) |
Average (μg/m3) |
|||
Reading 1 |
Reading 2 |
Reading 3 |
Average |
|||
1 |
3 Jan 2009 |
189 |
170 |
159 |
173 |
155 |
2 |
9 Jan 2009 |
153 |
163 |
165 |
160 |
|
3 |
15 Jan 2009 |
152 |
164 |
176 |
164 |
|
4 |
21 Jan 2009 |
161 |
176 |
172 |
170 |
|
5 |
29 Jan 2009 |
112 |
113 |
105 |
110 |
Table 8 24-Hour TSP Monitoring Results
Day |
Date |
24-hr TSP (μg/m3) |
1 |
3 Jan 2009 |
87 |
2 |
9 Jan 2009 |
76 |
3 |
15 Jan 2009 |
85 |
4 |
21 Jan 2009 |
77 |
5 |
29 Jan 2009 |
70 |
|
Average |
79 |
Noise monitoring results in terms of Leq(30min), L10(30min) L90(30min) measured at the designated noise monitoring location are summarized in Table 9. L10 and L90 represent sound levels that are exceeded 10% and 90% of the time respectively. Normally, L10 measurements can be considered as the average peak levels, whilst L90 levels can be considered as the average background noise levels.
During the reporting month, the minimum and maximum noise level measured at Yuet Wu Villa was 60.2dB(A) Leq(30min) and 62.2dB(A) Leq(30min) respectively with an average of 61.2dB(A) Leq(30min). No exceedance was recorded in this reporting period. Summary of noise monitoring record will be provided in Appendix E.
Table 9 Noise Monitoring Results
Day |
Date |
L10(30mins) (dB(A)) |
L90(30mins) (dB(A)) |
Leq(30mins) (dB(A)) |
1 |
3 Jan 2009 |
63.2 |
58.9 |
61.2 |
2 |
9 Jan 2009 |
63.9 |
59.2 |
62.2 |
3 |
15 Jan 2009 |
63.5 |
58.5 |
61.2 |
4 |
21 Jan 2009 |
63.5 |
58.2 |
61.2 |
5 |
29 Jan 2009 |
61.2 |
57.9 |
60.2 |
|
Average |
63.1 |
58.5 |
61.2 |
Weather data of the monitoring station were obtained from the nearest Hong Kong Observatory (HKO) Tuen Mun automatic weather station located at Tuen Mun Town Park (63 mPD). Table 10 summarizes the wind data during the monitoring dates. Wind record from HKO is shown in Appendix F.
Table 10 Summary of Weather Conditions during the Monitoring Period
Date |
Weather |
Prevailing Wind direction |
Daily Average Wind speed (m/s) |
3 Jan 2009 |
Sunny |
N |
1.61 |
9 Jan 2009 |
Sunny |
N |
3.20 |
15 Jan 2009 |
Sunny |
N |
1.85 |
21 Jan 2009 |
Cloudy |
N |
1.47 |
29 Jan 2009 |
Cloudy |
NW |
1.75 |
5 site inspections were conducted by the Environmental Team (ET) in this reported period. Major observations by the ET, actions by the Contractor and outcome are summarized in the Table 11.
Table 11 Summary of Site Inspections
|
Date |
Observations |
Action taken by Contractor |
Outcome |
1 |
2 Jan 2009 |
No outstanding observations during inspection. |
Contractor was required to keep up with the mitigation measures. |
|
2 |
10 Jan 2009 |
Stockpiles were compacted. |
The contractor was advised to cover the stockpiles after work. |
The situation was rectified after work immediately. |
3 |
15 Jan 2008 |
No outstanding observations during inspection. |
Contractor was required to keep up with the mitigation measures. |
|
4 |
22 Jan 2009 |
No outstanding observations during inspection. |
Contractor was required to keep up with the mitigation measures. |
|
5 |
30 Jan 2009 |
No outstanding observations during inspection. |
Contractor was required to keep up with the mitigation measures. |
|
During site inspections in the reporting month, no non-conformance of implementation of environmental mitigation measures was identified. All environmental mitigation measures for construction stages stated in approved EIA Report, EM&A Manual and Environmental Permit shall be carried out throughout the whole construction period as shown in Appendix G.
In this reporting period, no complaint, inspection notice, notification of summons or prosecution was received. No non-compliance was recorded.
4778.14 m3 of inert C&D waste was disposed at public fill. 6.31 tonnes of waste was disposed to landfill. No chemical waste was transported off site in this reporting period.
Environmental monitoring has been carried out for the proposed Joint User Complex and Wholesale Fish Market at Area 44, Tuen Mun. 1-hour and 24-hour TSP air quality monitoring and noise monitoring was conducted at Block 15, Yuet Wu Villa during the period from 1st January 2009 to 31st January 2009.
The average 1-hour TSP level is 155μg/m3 and average 24-hour TSP level is 79μg/m3. For impact noise monitoring, the 30-minute average noise level is 61.2dB(A).