Revision History
Rev. |
Description of Modification |
Date |
1 |
First Issue for Comments |
23/08/2023 |
2 |
Second Issue for Comments |
29/08/2023 |
CONTENTS
6. Summary of Exceedance, Complaints, Notification of Summons and Prosecitions.................... 22
Appendix A Master Programme
Appendix B Overview of Desalination Plant in Tseung Kwan O
Appendix C Summary of Implementation Status of Environmental Mitigation
Appendix D Water Quality Graphical Presentation
Appendix E Site Inspection Proforma
Appendix F Waste Flow Table
Appendix G Summary of Exceedances
Appendix H Complaint Log
Appendix I Event/Action Plan for Noise and Water Quality Monitoring Exceedance
A1. The Project, Design, Build and Operate First Stage of Tseung Kwan O Desalination Plant (TKODP), is a Designated Project under the Environmental Impact Assessment Ordinance (Cap. 499) (EIAO) and is currently governed by a Further Environmental Permit (EP No. FEP - 01/503/2015/A) for the construction and operation of the Contract.
A2. In accordance with the Environmental Monitoring and Audit (EM&A) Manual for the Contract, EM&A works for marine water quality, noise, waste management and ecology should be carried out by Environmental Team (ET), Acuity Sustainability Consulting Limited (ASCL), during the construction phase of the Contract.
A3. This is the 3rd Annual EM&A Review Report, prepared by ASCL, for the Contract summarizing the monitoring results and audit findings of the EM&A programme at and around Tseung Kwan O Area 137 (TKO 137) during the reporting period from 1 May 2022 to 30 April 2023.
A4. The EM&A programme for this contract has covered environmental monitoring on water quality, construction noise level at selected noise sensitive receivers, and Contractor’s environmental performance auditing in the aspects of construction dust, construction noise, water quality, waste management, landscape and visual and ecology.
A5. A summary of the environmental monitoring and audit works undertaken in the reporting period are summarized in Table I.
A6. No construction noise monitoring was conducted during the reporting period since there are no Contract -related construction activities undertaken within a radius of 300m from the monitoring locations. No Action Level exceedance was recorded during the reporting period.
A7. Water Quality Monitoring was conducted as schedule in the reporting period. Seven hundred and forty-four (744) action level exceedances and six hundred and eleven (611) limit level exceedances of Suspended Solid were recorded in the reporting period. Summary of exceedances could be referring to Appendix G.
A8. All Action and Limit Level exceedance was concluded to be unrelated to the Project. Details of the exceedance could be referring to Appendix O of the corresponding Monthly EM&A Report.
A9. Four hundred and twenty-four (424) times of landfill gas monitoring were conducted in the reporting period. No action or limit level exceedance was recorded in the reporting period.
Environmental Monitoring works |
Frequency |
Noise Monitoring |
N/A |
Water Quality Monitoring |
150 |
Landfill Gas Monitoring |
424 |
Environmental Site Inspection |
52 |
A10. One environmental complaint was received from the EPD in the reporting period, no notifications of summons and prosecution was received during the reporting period.
A11. There was no change to be reported that may affect the on-going EM&A programme.
1.1.
Background
The Jardine Engineering Corporation, Limited, China State Construction Engineering (Hong Kong) Limited and Acciona Agua, S.A. Trading as AJC Joint Venture (AJCJV) is contracted to carry out the Design, Build and Operate First Stage of Tseung Kwan O Desalination Plant (TKODP) under Contract No. 13/WSD/17 (the Contract).
Acuity Sustainability Consulting Limited (ASCL) is commissioned by AJCJV to undertake the Environmental Team (ET) services as required and/or implied, both explicitly and implicitly, in the Environmental Permit (EP), Environmental Impact Assessment Report (EIA Report) (Register No. AEIAR-192/2015) and Environmental Monitoring and Audit Manual (EM&A Manual) for the Contract; and to carry out the Environmental Monitoring and Audit (EM&A) programme in fulfillment of the EIA Report’s EM&A requirements and Contract No. 13/WSD/17 Specification requirements.
Pursuant to the Environmental Impact Assessment Ordinance (EIAO), the Director of Environmental Protection granted the Environmental Permit (No. EP-01/503/2015) and Variation of Environmental Permit (No. EP-01/503/2015/A) to Water Supplies Department (WSD); and granted the Further Environmental Permit (No. FEP- 01/503/2015/A) to AJCJV for the Contract.
1.2.
The Reporting Scope
This is the 3rd Annual EM&A Review Report for the Project which summarizes the key findings of the EM&A programme during the reporting period from 1 May 2022 to 30 April 2023.
1.3.
Contract Organization
The Contract Organization structure for Construction Phase is presented in Figure 1.1 and contact details of the key personnel are presented in Table 1.1 below:
Party |
Position |
Name |
Telephone no. |
Project Proponent (WSD) |
SE/CM2 |
Benny Lam |
2634-3573 |
Supervising Officer (Binnies Hong Kong Limited) |
Project Manager |
Christina Ko |
2608-7302 |
Chief Resident Engineer |
Roger Wu |
6343-1002 |
|
The Jardine Engineering Corporation, Limited, China State Construction Engineering (Hong Kong) Limited and Acciona Agua, S.A. Trading |
Project Manager |
Stephen Yeung |
2807-4665 |
Environmental Monitoring Manager |
Brian Kam |
9456-9541 |
|
Acuity Sustainability Consulting Limited |
Environmental Team Leader (ETL) |
Jacky Leung |
2698-6833 |
ANewR Consulting Limited |
Independent Environmental Checker (IEC) |
Louis Kwan |
2618-2831 |
1.4.
Summary of Construction Works
The construction programme is presented in Appendix A. Detail of the major construction activities undertaken could be referred to Section 1.4 in each monthly EM&A Report.
The status for all environmental aspects is presented in Table 1.2.
Parameters |
Status |
Water Quality |
|
Baseline Monitoring under EM&A Manual |
The baseline water quality monitoring was conducted between 12 May 2020 to 6 Jun 2020 |
Impact Monitoring |
On-going |
Noise |
|
Baseline Monitoring |
The baseline noise monitoring result has been reported in Baseline Monitoring Report and submitted to EPD under EP Condition 3.4. |
Impact Monitoring |
On-going |
Waste Management |
|
Mitigation Measures in Waste Management Plan |
On-going |
Environmental Audit |
|
Site Inspection covering Measures of Air Quality, Noise Impact, Water Quality, Waste, Ecological Quality, Fisheries, Landscape and Visual |
On-going |
Other than the EM&A work by ET, environmental briefings, trainings and regular environmental management meetings were conducted, in order to enhance environmental awareness and closely monitor the environmental performance of the contractors.
The EM&A programme has been implemented in accordance with the recommendations presented in the approved EIA Report and the EM&A Manual. A summary of implementation status of the environmental mitigation measures for the construction phase of the Contract during the reporting period is provided in Appendix C.
2.1.
Monitoring Requirements
To ensure no adverse noise impact, noise monitoring is recommended to be carried out within 300m radius from the nearby noise sensitive receivers (NSRs), during construction phase. The NSRs selected as monitoring station are (i) NSR4 - Creative Secondary School, (ii) NSR24 - PLK Laws Foundation College, and (iii) NSR31 - School of Continuing and Professional Studies - CUHK respectively.
2.2.
Monitoring Locations
The monitoring locations were normally made at a point 1m from the exterior of the NSRs building façade and be at a position 1.2m above the ground. A correction of +3dB(A) was made to the free-field measurements.
According to the environmental findings detailed in the EIA report and Baseline Monitoring Report, the designated locations for the construction noise monitoring are listed in Table 2.1 below.
NSR ID |
Noise Sensitive Receivers |
Monitoring Location |
Position |
NSR 4 |
Creative Secondary School |
Roof Floor |
1 m from facade |
NSR 24 |
PLK Laws Foundation College |
Pedestrian Road on Ground Floor |
Free field |
NSR 31 |
School of Continuing and Professional Studies - CUHK |
Roof Floor |
1 m from facade |
Three noise monitoring locations for impact monitoring at the nearby sensitive receivers are shown in Figure 2.1-2.3.
|
Figure 2.1 NSR4
Creative Secondary School |
|
Figure 2.2 NSR24 PLK Laws Foundation College |
|
Figure 2.3 NSR31
School of Continuing and Professional Studies - CUHK |
2.3.
Monitoring Parameter, frequency and duration
Construction noise level were measured in terms of the A-weighted equivalent continuous sound pressure level (LAeq). Leq 30min was used as the monitoring parameter for the time period between 0700 and 1900 on normal weekdays. Table 2.2 summarizes the monitoring parameters, frequency, and duration of the impact noise monitoring.
Time |
Duration |
Interval |
Parameters |
Daytime: 0700-1900 |
Day time: 0700-1900 (during normal weekdays) |
Continuously in Leq 5min/Leq 30min (Average of 6 consecutive Leq 5min) |
Leq 30min
L10 30min & L90 30min |
2.4.
Impact Monitoring Methodology
The monitoring methodology and QA/QC procedure could be referring to Section 2.3 of the Monthly EM&A Report.
2.5.
Action and Limit
Levels
The Action/Limit Levels are in line with the criteria of Practice Note for Professional Persons (ProPECC PN 2/93) “Noise from Construction Activities - Non-statutory Controls” and Technical Memorandum on Environmental Impact Assessment Process issued by HKSAR Environmental Protection Department [“EPD”] under the Environmental Impact Assessment Ordinance, Cap 499, S.16 are presented in Table 2.3.
Time Period |
Action |
Limit (dB(A)) |
0700-1900 on normal weekdays |
When one documented complaint is received from any one of the noise sensitive receivers |
- 70 dB(A) for school and - 65 dB(A) during examination period |
Notes: Limits specified in the GW-TM
and IND-TM for construction and operation noise,
respectively.
If exceedances were found during noise monitoring, the actions in accordance with the Event and Action Plan shall be carried out according to Appendix E.
2.6.
Monitoring Results and Observations
Referring to EM&A manual Section 4.1.2, the impact noise monitoring should be carried out when there are Contract-related construction activities undertaken within a radius of 300m from the monitoring stations. No monitoring station was located within a radius of 300m of the Contract site as shown in Figure 2.4, no impact monitoring for noise impact was conducted in the reporting period.
In accordance with the recommendations of the EIA, water quality EM&A is required during dredging for the submarine pipelines and, during operation phase. In addition, baseline water quality monitoring was prior to the commencement of marine construction activities.
The following Section provides details of the water quality monitoring to be undertaken by the Environmental Team (ET) to verify the distance of sediment and brine plume dispersion and to identify whether the potential exists for any indirect impacts to occur to ecological sensitive receivers.
Water quality monitoring for the Contract can be divided into the following stages:
- Dredging activities during construction phase;
- Discharge of effluent from main disinfection during construction phase;
- Operation phase - first year upon commissioning; and,
- Continuous monitoring of effluent quality.
In addition, the marine works contractor is required to complete a silt curtain efficiency test for the combined use of floating silt curtain type and cage type silt curtain for dredging at seawater intake to confirm the silt curtain reduction efficiency assumptions of the assessment. The details of testing plan together with the silt curtain deployment plan shall be submitted by the ET to seek approval from the IEC and EPD.
3.1.
Water Quality Parameters
The parameters that have been selected for measurement in situ and in the laboratory are those that were either determined in the EIA to be those with the most potential to be affected by the construction works or are a standard check on water quality conditions. Parameters to be measured in the impact water quality monitoring are listed in Table 3.1.
Parameters |
Unit |
Abbreviation |
In-situ measurements |
||
Dissolved oxygen |
mg/L |
DO |
Temperature |
oC |
- |
pH |
- |
- |
Turbidity |
NTU |
- |
Salinity |
0/00 |
- |
Laboratory measurements |
||
Suspended Solids |
mg/L |
SS |
NOTE 1: Monitoring of TRC will be
conducted when cleaning
and sterilization of the new freshwater main is carried
out.
In addition to the water quality parameters, other relevant data was measured and recorded in Water Quality Monitoring Logs, including the location of the sampling stations, water depth, time, weather conditions, sea conditions, tidal stage, current direction and velocity, special phenomena and work activities undertaken around the monitoring and works area that may influence the monitoring results.
3.2.
Monitoring Equipment
The monitoring methodology, monitoring equipment and QA/QC procedure could be referring to Section 3.1.2 - 3.1.4 of the Monthly EM&A Report.
3.3.
Monitoring Location
The impact water quality monitoring locations are in accordance with the EM&A Manual and detailed in Table 3.3 below.
Station |
Easting |
Northing |
Description |
CE |
843550 |
815243 |
Upstream control station at ebb tide |
CF |
846843 |
810193 |
Upstream control station at flood tide |
WSR1 |
846864 |
812014 |
Ecological sensitive receiver at Tung Lung Chau |
WSR2 |
847645 |
812993 |
Fisheries sensitive receiver at Tung Lung Chau |
WSR3 |
848023 |
813262 |
Ecological sensitive receiver at Tung Lung Chau |
WSR4 |
847886 |
814154 |
Ecological sensitive receiver at Tai Miu Wan |
WSR16 |
845039 |
815287 |
Ecological sensitive receiver at Fat Tong Chau |
WSR33 |
847159 |
814488 |
Ecological sensitive receiver at Tai Miu Wan |
WSR36 |
846878 |
814081 |
Ecological sensitive receiver at Kwun Tsai |
WSR37 |
846655 |
813810 |
Ecological sensitive receiver at Tit Cham Chau |
NF1 |
846542 |
813614 |
Edge of mixing zone, ~ 200m west of outfall diffuser |
NF2 |
846942 |
813614 |
Edge of mixing zone, ~ 200m east of outfall diffuser |
NF3 |
846742 |
813414 |
Edge of mixing zone, ~ 200m south of outfall diffuser |
WSR1 to WSR37 were identified in accordance with Annex 14 of the EIAO-TM as well as Clause 3.4.4.2 of the Environmental Impact Assessment Study Brief for Desalination Plant at Tseung Kwan O (No. ESB-266/2013). WSR1 to WSR3 are sited near the Tung Lung Chau Fish Culture Zone; WSR16 and WSR36 are sited near the coral assemblages along the
coastlines of Fat Tong Chau and Kwun Tsai respectively; WSR 4 and WSR33 are sited near the Coastal Protection Area and coral assemblages in waters of Tai Miu Wan; WSR37 is sited near the fisheries resource including spawning and nursery grounds at the coastal water of Tit Cham Chau.
3.4.
Action and Limit
levels
The Action and Limit Levels have been set based on the derivation criteria specified in the EM&A Manual. Based on the baseline water quality monitoring data and the derivation criteria, the Action/Limit Levels have been derived and are presented in Table 3.4.
Parameters |
Action |
Limit |
Construction Phase Impact
Monitoring |
||
DO in mg/L |
Surface and Middle 7.30 mg L-1 Bottom 7.31 mg L-1 Tung Lung Chau Fish Culture Zone 5.1 mgL-1 or level at control station (whichever the lower) |
Surface and Middle 4 mg
L-1 Bottom 2 mg L-1 Tung Lung Chau Fish Culture Zone 5.0 mgL-1 or level at control station (whichever the lower) |
SS in mg/L (Depth- averaged) |
5.00 mg L-1 or 20% exceedance of value at any impact station compared with corresponding data from control station |
6.00 mg L-1 or 30% exceedance of value at any impact station compared with corresponding data from control station |
Turbidity in NTU (Depth-averaged) |
2.41 NTU or 20% exceedance of value at any impact station compared with corresponding data from control station |
2.84 NTU or 30% exceedance of value at any impact station compared with corresponding data from control station |
Notes:
i. "Depth-averaged" is calculated by taking the arithmetic means
of reading of all three depths.
ii. For DO, non-compliance of the water quality limits
occurs when monitoring result is lower
than the limits.
iii. For Turbidity, SS, iron and Salinity,
non-compliance of the water quality
limits occurs when monitoring result is higher than the limits.
iv. For the Action and Limit Levels adopted during
First-year Operation Phase
Monitoring, further review
would be made according to the EM&A Manual during Operation Phase.
3.5.
Monitoring Programme
The ET of the Contract had conducted the impact water quality monitoring between 1 May 2022 to 30 April 2023 at the ten designated monitoring stations at waters near TKO in accordance with the EM&A Manual and Contract Specification respectively.
3.6.
Monitoring results and observations
The impact water quality monitoring at the designated locations were conducted by the ET as scheduled in the reporting period. The graphical presentation of the water quality monitoring result was shown in Appendix D.
Seven hundred and forty-four (744) of the general water quality monitoring results of SS obtained had exceeded the Action level. Six hundred and eleven (611) of the general water quality monitoring results of SS obtained during the reporting period had exceeded the Limit Level.
Details of the exceedance could be referring to Appendix O of the Monthly EM&A Report.
The waste generated from this Project includes inert construction and demolition (C&D) materials, and non-inert C&D materials. Non-inert C&D materials are made up of general refuse, vegetative wastes and recyclable wastes such as plastics and paper/cardboard packaging waste. Steel materials generated from the project are also grouped into non-inert C&D materials as the materials were not disposed of with other inert C&D materials. Details of cumulative waste management data are presented as a waste flow table in Appendix F.
5.1.
Monitoring Requirement
In according with Section 11 of the EM&A Manual, monitoring of landfill gas is required for construction works within the 250m Consultation Zone. Part of the desalination plant and the indicative area of natural slope mitigation works fall within the SENT Landfill Extension Consultation Zone; and part of the 1,200 mm diameter freshwater mains along Wan Po Road falls within the SENT Landfill and SENT Landfill Extension Consultation Zones, TKO Stage II/III Restored Landfill and TKO Stage I Restored Landfill Consultation Zones.
Since part of the desalination plant (Wan Po Road and MIC compound/Basketball Court) and the indicative area of natural slope mitigation works fall within the SENT Landfill Extension Consultation Zone in this contract (Figure 5.1), landfill gas monitoring would be required for Wan Po Road and MIC compound/Basketball Court (Figure 5.2) if excavations were conducted at more than 300mm deep. Although SENT Landfill Extension has commenced operation since November 2021, no excavation works were conducted at MIC compound/Basketball Court. Hence no landfill gas monitoring would be scheduled for MIC compound/Basketball Court at the current stage.
5.2.
Monitoring Parameters
LFG monitoring was carried out to identify any migration between the landfill and the Contract and to ensure the safety of the construction, operation and maintenance personnel working on-site, visitors and any other person within the Contract area.
The following parameters were monitored:
- Methane
- Oxygen
- Carbon Dioxide
- Barometric Pressure
5.3.
MONITORING EQUIPMENT
Landfill Gas monitoring was carried out using intrinsically safe, portable multi-gas monitoring instruments. Detail of monitoring equipment used in the reporting period could be referred to Section 5.10 of the corresponding Monthly EM&A Report.
5.4.
Monitoring results and observations
Four hundred and twenty-four (424) times of landfill gas monitoring were conducted in the reporting period. No action or limit level exceedance was recorded in the reporting period.
Action and Limit Level are provided in Table 5.1.
Parameters |
Level |
Action |
Oxygen (O2) |
Action Level <
19% O2 Limit Level < 19% O2 |
Ventilate trench/void to restore
O2 to > 19% Stop works |
|
|
Evacuate personnel/prohibit entry |
|
|
Increase
ventilation to restore
O2 to > |
|
|
19% |
Methane (CH4) |
Action Level >10% LEL |
Post "No Smoking" signs |
|
|
Prohibit hot works |
|
|
Increase ventilation to restore CH4 to |
|
|
<10% LEL |
|
Limit Level >20% LEL |
Stop works |
|
|
Evacuate personnel/prohibit entry |
|
|
Increase ventilation to restore |
|
|
CH4 to<10% LEL |
Carbon Dioxide (CO2) |
Action Level >0.5% CO2 |
Ventilate to restore CO2 to < 0.5% |
|
Limit Level >1.5% CO2 |
Stop works |
|
|
Evacuate personnel / prohibit entry |
|
|
Increase ventilation to restore CO2 to |
|
|
<0.5% |
6.
SUMMARY OF EXCEEDANCE, COMPLAINTS, NOTIFICATION
OF SUMMONS AND
Prosecutions
The Environmental Complaint Handling Procedure is shown in below Figure 6.1:
No noise monitoring was conducted during the reporting period since there are no Contract-related construction activities undertaken within a radius of 300m from the monitoring locations.
Seven hundred and forty-four (744) of the general water quality monitoring results of SS obtained had exceeded the Action level. Six hundred and eleven (611) of the general water quality monitoring results of SS obtained during the reporting period had exceeded the Limit Level.
Details of the exceedance could be referring to Appendix O of the corresponding Monthly Report.
Four hundred and twenty-four (424) times of landfill gas monitoring were conducted in the reporting period. No action or limit level exceedance was recorded in the reporting period.
One environmental complaint was received from EPD on 22 July 2022 in the reporting period. Detailed information could be referred to the Monthly EM&A Report in July 2022. No notification of summons and prosecution was received in the reporting period. Summary of complaint log are presented in Appendix J.
Site inspections were carried out on a weekly basis to monitor the implementation of proper environmental pollution control and mitigation measures under the Contract. In the reporting period, site inspections were carried out from May 2022 to April 2023.
Fifty-two (52) site inspection were carried out in the reporting period.
Environmental deficiencies were observed during weekly site inspection. Key observations during the site inspections and during the reporting period could be referring to Appendix E and corresponding Monthly Report.
According to the EIA Study
Report, Environmental Permit, contract documents and EM&A Manual, the
mitigation measures detailed in the documents should be implemented as much as
practical during the reporting period. An updated Implementation Status of
Environmental Mitigation Measures (EMIS) is provided in Appendix C.
This is the 3rd Annual EM&A Review Report for the Project which summarizes the key findings of the EM&A programme during the reporting period from 1 May 2022 to 30 April 2023, in accordance with the EM&A Manual and the requirement under FEP- 01/503/2015/A.
No noise monitoring was conducted in the reporting period due to the over distant monitoring station from the works location, in which construction activities were not undertaken within a radius of 300m from the monitoring locations.
The EM&A works for water quality were conducted during the reporting period in accordance with the EM&A Manual.
Seven hundred and forty-four (744) of the general water quality monitoring results of SS obtained had exceeded the Action level. Six hundred and eleven (611) of the general water quality monitoring results of SS obtained during the reporting period had exceeded the Limit Level. All Action and Limit Level exceedances were unrelated to the project.
Details of the exceedance could be referring to Appendix O of the corresponding Monthly EM&A Report.
Four hundred and twenty-four (424) times of landfill gas monitoring were conducted in the reporting period. No action or limit level exceedance was recorded in the reporting period.
Weekly environmental site inspection was conducted during the reporting period. Minor deficiency was observed during site inspection. The environmental performance of the project was therefore considered satisfactory.
According to the environmental site inspections performed in the reporting period, the Contractor is reminded to pay attention on maintaining proper materials storage, site tidiness and chemical storage on site.
One environmental complaint was received from EPD on 22 July 2022 in the reporting period. Detailed information could be referred to the Monthly EM&A report in July 2022. No notification of summons or prosecution was received in the reporting period.
The ET will keep track on the construction works to confirm compliance of environmental requirements and the proper implementation of all necessary mitigation measures.
Appendix A
Master Programme
Appendix B
Overview of Desalination Plant in Tseung Kwan O
Appendix C
Summary of Implementation Status of Environmental Mitigation
EIA Reference |
Recommended Environmental
Protection Measures/ Mitigation Measures |
Objectives of
the recommended measures
& main concerns to address |
Implementation Agent |
Implementation Stage |
Implementation status |
Relevant Legislation & Guidelines |
||
D |
C |
O |
||||||
Air Quality |
|
|||||||
S4.8.1 |
Impervious dust screen or
sheeting will be provided to enclose scaffolding from the ground
floor level of building for construction of superstructure of
the new buildings. |
Land site/ During Construction |
Contractor(s) |
|
ü |
|
Implemented |
Air Pollution Control (Construction Dust) |
S4.8.1 |
Impervious sheet
will be provided for skip hoist
for material transport. |
Land site/ During Construction, particularly dry season |
Contractor(s) |
|
ü |
|
NA |
- |
S4.8.1 |
The area
where dusty work
takes place should
be sprayed with water or a dust
suppression chemical immediately prior
to, during and immediately after dusty activities as far as practicable. |
Land site/ During Construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S4.8.1 |
All dusty materials should be sprayed
with water or a dust suppression
chemical immediately prior to any loading,
unloading or transfer operation. |
Land site/ During Construction |
Contractor(s) |
|
ü |
|
Implemented, reminder issued |
- |
S4.8.1 |
Dropping heights for excavated materials should be controlled to a practical height to
minimize the fugitive dust arising
from unloading. |
Land site/ During Construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S4.8.1 |
During transportation by truck, materials should
not be loaded to a level higher
than the side and tail boards and should
be dampened or covered before transport. |
Land site/ During Construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S4.8.1 |
Wheel washing device should be provided at the exits of the work sites.
Immediately before leaving a construction site, every vehicle shall be washed to
remove any dusty material from its
body and wheels as far as practicable. |
Land site/ During Construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S4.8.1 |
Road sections between
vehicle-wash areas and vehicular entrance
will be paved. |
Land site/ During Construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S4.8.1 |
Hoarding of not less
than 2.4m high from ground
level will be provided along
the length of the
Project Site boundary. |
Land site/ During
construction |
Contractor(s) |
ü |
ü |
|
N/A |
- |
S4.8.1 |
Haul roads will be kept clear of dusty materials and will be sprayed
with water so as to maintain the entire road
surface wet at all times. |
Land site/
During construction |
Contractor(s) |
|
ü |
|
Implemented, reminder issued |
- |
EIA Reference |
Recommended Environmental
Protection Measures/ Mitigation Measures |
Objectives of
the recommended measures
& main concerns to address |
Implementation Agent |
Implementation Stage |
Implementation status |
Relevant Legislation & Guidelines |
||
D |
C |
O |
||||||
S4.8.1 |
Temporary stockpiles of dusty materials will be either covered entirely by impervious sheets or
sprayed with water to maintain the
entire surface wet all the time. |
Land site/
During construction |
Contractor(s) |
|
ü |
|
Implemented, reminder issued |
- |
S4.8.1 |
Stockpiles of more than
20 bags of cement, dry pulverised fuel ash and dusty
construction materials will be covered entirely by impervious sheeting
sheltered on top and 3- sides. |
Land site/ During
construction |
Contractor(s) |
|
ü |
|
N/A |
- |
S4.8.1 |
All exposed
areas will be kept wet always to minimize dust emission. |
Land site/ During
construction |
Contractor(s) |
|
ü |
|
Implemented, reminder issued |
- |
S4.8.1 |
Ultra-low-sulphur diesel (ULSD) will be
used for all construction plant
on-site, as defined as diesel fuel containing
not more than 0.005% sulphur by weight) as stipulated in Environment, Transport and
Works Bureau Technical Circular
(ETWB-TC(W)) No 19/2005 on Environmental
Management on Construction Sites. |
Land site/ During construction/ During Operation |
Contractor(s) |
|
ü |
ü |
Implemented |
Environment, Transport and Works Bureau
Technical Circular (ETWB-
TC(W)) No 19/2005 on Environmental Management on Construction Sites |
S4.8.1 |
The engine
of the construction equipment during idling
will be switched off. |
Land site/ During
construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S4.8.1 |
Concrete batching plant will be required on site. control measures recommended in the Guidance
Note on a Best Practicable Means
for Cement Works (Concrete Batching Plant)
(BPM 3/2 (93)) will be implemented. The control measures recommended in the Guidance Note on a Best Practicable Means for Cement Works
(Concrete Batching Plant) (BPM 3/2
(93)) will be implemented. |
Land site/
During construction |
Contractor(s) |
|
ü |
|
N/A |
- |
S4.8.1 |
Regular maintenance of construction equipment deployed on-site
will be conducted to prevent black smoke emission. |
Land site/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S4.10 |
To ensure proper implementation of the recommended dust mitigation measures and good
construction site practices during
the construction phase, environmental site audits
on weekly basis is recommended throughout the construction period. |
Land site/ During
construction |
Contractor(s)/ ET & IEC |
|
ü |
|
Implemented |
|
Note: D - Design stage C - Construction O - Operation
EIA Reference |
Recommended Environmental
Protection Measures/ Mitigation Measures |
Objectives of the recommended measures & main concerns to address |
Implementation Agent |
Implementation Stage |
Implementation status |
Relevant Legislation & Guidelines |
||
D |
C |
O |
||||||
Noise |
||||||||
S5.7 |
Only well-maintained plant will be operated on-site and plant will be serviced regularly during
the construction phase. |
All area/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
A Practical Guide for the Reduction of Noise from |
S5.7 |
Silencers or mufflers on construction equipment will be utilised and will be properly maintained during the |
Noise control/ During construction |
Contractor(s) |
|
ü |
|
N/A |
Construction Works |
|
construction phase. |
|
|
|
|
|
||
S5.7 |
Mobile plant,
if any, will
be sited as far away from NSRs
as possible. |
Noise control/ During construction |
Contractor(s) |
|
ü |
|
N/A |
|
S5.7 |
Machines and plant
(such as trucks)
that may be in intermittent use will be shut down between work periods |
Noise control/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
|
|
or will be throttled down
to a minimum. |
|
|
|
|
|
||
S5.7 |
Plants known to emit noise strongly in one
direction will, wherever possible, be orientated so that the
noise is |
Noise control/ During construction |
Contractor(s) |
|
ü |
|
N/A |
|
|
directed away from the nearby
NSRs. |
|
|
|
|
|
||
S5.7 |
Material stockpiles and other structures will be effectively utilised, wherever practicable, in screening noise
from on- |
Noise control/ During construction |
Contractor(s) |
|
ü |
|
N/A |
|
|
site construction activities. |
|
|
|
|
|
||
S5.7 |
Use of Quite Powered Mechanical Equipment (QPME). |
Noise control/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
|
S5.7 |
Movable noise barriers of 3m in height with skid footing should be used and located within
a few metres of stationary plant and mobile plant
such that the line of sight |
Noise control/ During construction |
Contractor(s) |
|
ü |
|
N/A |
|
|
to the NSR is blocked by the barriers. The length of the |
|
|
|
|
|
||
|
barrier should be at least
five times greater than its height. |
|
|
|
|
|
||
|
The noise barrier material should have a superficial surface |
|
|
|
|
|
||
|
density of at least 7 kg m-2 and have
no o or gappeningss. |
|
|
|
|
|
||
S5.7 |
The noise insulating sheet should be deployed such that |
Noise control/ During |
Contractor(s) |
|
ü |
|
N/A |
|
there would be no opening or gaps on the joints. |
construction |
|
|
|||||
S5.7 |
Construction activities (e.g. excavation/shoring, reinstatement (asphalt), and pipe
jacking) will be
planned |
Noise control/ During construction |
Contractor(s) |
ü |
ü |
|
Implemented |
|
|
and carried out in sequence, such that items
of PME |
|
|
|
|
|
|
|
|
proposed for these activities will not be operated |
|
|
|
|
|
|
|
|
simultaneously. |
|
|
|
|
|
|
EIA Reference |
Recommended Environmental
Protection Measures/ Mitigation Measures |
Objectives of the recommended measures & main concerns to address |
Implementation Agent |
Implementation Stage |
Implementation status |
Relevant Legislation & Guidelines |
||
D |
C |
O |
||||||
S5.7 |
PMEs will
not be used
at the works
areas near educational institutions with residual impact (ie
the “influence area” within a
radius of 40m) during school hours in order to reduce impact to the educational institutions. |
Noise control
/ During construction |
Contractor(s) |
|
ü |
|
N/A |
|
S5.7 |
Noise enclosures or acoustic sheds
would be used
to cover stationary PME such as generators.
Portable/Movable noise enclosure
made of material with superficial surface density
of at least 7 kg m-2 may be used for screening the noise from operation of the saw/groover, concrete. |
Noise control/ Pre- construction/ During construction |
Contractor(s) |
ü |
ü |
|
N/A |
- |
S5.9 |
Sawcutting pavement,
breaking up of pavement, excavation /shoring, pipe laying, backfilling,
reinstatement (concrete) and pipe jacking
shall be scheduled outside the examination period. |
Noise control/ Pre- construction/ During construction |
Contractor(s) |
ü |
ü |
|
N/A |
-- |
S5.9 |
In view the duration of noise exceedance at Creative Secondary School, PLK Laws Foundation College, TKO Kei Tak Primary
School and School of Continuing and Professional
Studies-CUHK is limited to 8 weeks, the construction
work in the influence areas near the four schools
shall be scheduled during long school holidays (e.g., summer
holiday, Easter holiday
or Christmas holiday, etc.) as far as practicable. Scheduling the construction work for the four
schools. |
Noise control/ Pre- construction/ During construction |
Contractor(s) |
ü |
ü |
|
N/A |
- |
S5.10 |
A noise monitoring programme shall be implemented for the construction phase. |
Designated monitoring stations as defined in EM&A Manual/During construction phase |
ET |
|
ü |
|
N/A |
- |
S5.10 |
The effectiveness of on-site
control measures could
also be evaluated through the regular site
audits. |
All facilities/ During construction |
Contractor(s)/ ET & IEC |
|
ü |
|
Implemented |
- |
Note: D - Design stage C - Construction O - Operation
EIA Reference |
Recommended Environmental
Protection Measures/ Mitigation Measures |
Objectives of the recommended measures & main concerns to address |
Implementation Agent |
Implementation Stage |
Implementation status |
Relevant Legislation & Guidelines |
||
D |
C |
O |
||||||
Water Quality |
||||||||
S6.9 |
Dredged marine sediment will be disposed of in a gazetted marine
disposal area in accordance with marine dumping permit conditions of
the Dumping at Sea Ordinance (DASO). |
Marine Dredging/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
Dumping at Sea Ordinance (DASO) |
S6.9 |
Disposal vessels will be fitted with tight
bottom seals in order
to prevent leakage of material during transport. |
Marine Dredging/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S6.9 |
Barges will be filled to a level,
which ensures that
material does not spill over during transport to the disposal site and that adequate freeboard is maintained to ensure that the decks are not washed by wave action. |
Marine Dredging/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S6.9 |
After dredging, any excess
materials will be cleaned from decks
and exposed fittings before the vessel
is moved from
the dredging area. |
Marine Dredging/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S6.9 |
All vessels should be well maintained and inspected before
use to limit any potential discharges to the marine environment. |
Marine Dredging/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S6.9 |
All vessels must
have a clean
ballast system. |
Marine Dredging/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S6.9 |
No discharge of sewage/grey wastewater should be allowed. Wastewater from potentially contaminated area on
working vessels should be minimized and collected. These
kinds of wastewater should be brought back to port and
discharged at appropriate collection
and treatment system. |
Marine Dredging/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S6.9 |
No soil waste is allowed to be disposed overboard. |
Marine Dredging/ During construction |
Contractor(s) |
|
ü |
|
N/A |
- |
EIA Reference |
Recommended Environmental
Protection Measures/ Mitigation Measures |
Objectives of the recommended measures & main concerns to address |
Implementation Agent |
Implementation Stage |
Implementation status |
Relevant Legislation & Guidelines |
||
D |
C |
O |
||||||
S6.9 |
Silt
removal facilities such as silt traps or sedimentation facilities will be provided to remove silt particles from runoff to meet the requirements of the TM standard under
the WPCO. The design of silt removal
facilities will be based on the guidelines provided in ProPECC PN 1/94. All drainage
facilities and erosion and sediment
control structures will be inspected on a regular basis and maintained to confirm proper
and efficient operation at all times
and particularly during
rainstorms. Deposited silt and grit
will be removed
regularly. |
Land site &
drainage/ During construction |
Contractor(s) |
|
ü |
|
Implemented reminder issued |
ProPECC PN 1/94 TM Standard under the WPCO |
S6.9 |
Earthworks to form the final surfaces will be followed up with surface protection and drainage
works to prevent erosion caused by
rainstorms. |
Land site & drainage/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S6.9 |
Appropriate surface
drainage will be designed and provided
where necessary. |
Land site &
drainage/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S6.9 |
The precautions
to be taken at any time of year when rainstorms are
likely together with
the actions to be taken
when a rainstorm is imminent or forecasted and actions to be
taken during or after rainstorms are summarized in Appendix A2 of ProPECC PN 1/94. |
Land site &
drainage/ During construction |
Contractor(s) |
ü |
ü |
|
Implemented |
ProPECC PN 1/94 |
S6.9 |
Oil interceptors will be provided in the drainage system where necessary and regularly emptied to
prevent the release of oil and
grease into the storm water drainage system
after accidental spillages. |
Land site &
drainage/ During construction |
Contractor(s) |
|
ü |
|
N/A |
- |
S6.9 |
Temporary and
permanent drainage pipes and culverts provided
to facilitate runoff discharge, if any, will be adequately designed for the controlled release of storm flows. |
Land site &
drainage/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S6.9 |
The temporary diverted drainage, if any, will
be reinstated to the original condition when the construction
work has finished or when the
temporary diversion is no longer required. |
Land site & drainage/ During construction |
Contractor(s) |
|
ü |
|
N/A |
- |
EIA Reference |
Recommended Environmental
Protection Measures/ Mitigation Measures |
Objectives of the recommended measures & main concerns to address |
Implementation Agent |
Implementation Stage |
Implementation status |
Relevant Legislation & Guidelines |
||
D |
C |
O |
||||||
S6.9 |
Appropriate numbers of portable toilets shall be provided by a licensed contractor to serve
the construction workers
over the construction site to prevent direct disposal of sewage into the water environment. |
Land site &
drainage/ During construction |
Contractor(s) |
|
ü |
|
Implemented |
- |
S6.9 and S6.12 |
The sterilization water
should be dechlorinated with total residual chlorine (TRC) level below 1
mg/L before discharge to public
sewer. In situ
testing of TRC should
also be conducted for the discharge of chlorinated water for pipeline disinfection to ensure
sufficient dichlorination before
discharge to public sewer. |
Sterilization of water mains prior to commissioning |
Contractor(s) |
|
ü |
ü |
N/A |
Technical Memorandum for Effluents Discharged into Drainage and Sewerage Systems |
S6.9 |
The cleaning and flushing water
should also be treated and desilted
to the relevant discharge requirement stipulated in TM-DSS before discharging. |
Sterilization of water mains prior to commissioning |
Contractor(s) |
|
ü |
ü |
Implemented, observation issued |
Technical Memorandum for Effluents Discharged into Drainage and |
S6. |