Expansion of Hong Kong International Airport into a Three-Runway System |
Contents
Executive summary
The “Expansion of Hong Kong International Airport into a Three-Runway System” (the Project) serves to meet the future air traffic demands at Hong Kong International Airport (HKIA). On 7 November 2014, the Environmental Impact Assessment (EIA) Report (Register No.: AEIAR-185/2014) for the Project was approved and an Environmental Permit (EP) (Permit No.: EP-489/2014) was issued for the construction and operation of the Project.
Airport Authority Hong Kong (AAHK) commissioned Mott MacDonald Hong Kong Limited (MMHK) to undertake the role of Environmental Team (ET) for carrying out the Environmental Monitoring & Audit (EM&A) works during the construction phase of the Project in accordance with the Updated EM&A Manual.
The commencement of initial reclamation works was announced on 1 August 2016. This is the 3rd Construction Phase Quarterly EM&A Report for the Project which summarizes the monitoring results and audit findings of the EM&A programme during the reporting period from 1 July 2016 to 30 September 2016.
Key Activities in the Reporting Period
Key activities of the Project carried out in the reporting period were related to the following contracts:
Advanced works Contract:
Contract P560 (R) Aviation Fuel Pipeline Diversion Works
· Installation of horizontal directional drilling (HDD) casing;
· Pilot hole drilling using HDD method at launching site;
· Stockpiling of excavated materials from HDD operation at stockpiling area; and
· Site preparation works and construction of containment pit at Sheung Sha Chau.
DCM Contracts:
Contract 3201 to 3204 Deep Cement Mixing Works
· Mobilization and off-site plant fabrication;
Other Contracts:
Contract 3213 CLP Cable Diversion Enabling Works
· Site preparation works at the western part of the airport.
EM&A Activities Conducted in the Reporting Period
The EM&A programme was undertaken in accordance with the Updated EM&A Manual of the Project. A summary of the monitoring and audit activities during this reporting period is presented as below:
Monitoring/ Audit Activities |
Number of Sessions |
1-hour Total Suspended Particulates (TSP) Air Quality Monitoring |
99 |
Noise Monitoring |
65 |
Water Monitoring |
25 |
Ecological Monitoring |
2 |
Vessel line-transect surveys for Chinese White Dolphin (CWD) monitoring |
4 |
Land-based theodolite tracking survey effort for CWD monitoring |
10 |
Note: No marine construction work was carried out during the reporting quarter, monitoring for water quality and CWD was conducted as scheduled.
|
|
|
Vessel Line-Transect Surveys for CWD Monitoring |
Skypier Plan Briefing at Integrated Airport Centre |
Construction Vessel Skipper Training |
In total, 2,459 ferry movements between HKIA SkyPier and Zhuhai / Macau were audited in the reporting period. All the High Speed Ferries (HSFs) had travelled through the Speed Control Zone (SCZ) with prevailing speed within 15 knots, which complied with the SkyPier Plan. Fifteen ferry movements had minor deviation from the diverted route during the reporting period. Among the 15 cases, eight cases are related to public safety / emergency situations. Follow-up actions such as checking of electronic marine chart / radar graphs and refresher training have been taken for the remaining non-public safety / emergency cases.
The audit of construction and associate vessels starts in August. ET has conducted weekly audit of relevant information to ensure sufficient information has been provided by the contractors to the Marine Traffic Control Center (MTCC) and the contractors are fully complied with the requirements of the Marine Travel Routes and Management Plan for Construction and Associated Vessel (MTRMP-CAV). A total of 11 skipper training workshops have been held in August and September with concerned captains of construction vessels associated with Contract P560(R) Aviation Fuel Pipeline Diversion Works and the four DCM contracts to familiarise them with the MTRMP-CAV.
Review of Environmental Quality Performance Limits (Action and Limit levels)
The water quality monitoring and CWD monitoring were completed as scheduled in August and September 2016, although no marine construction works was carried out in the reporting period.
For air quality, three exceedance cases involving Action Level of 1-hour TSP monitoring were recorded on 27 September 2016. The investigation results indicated that the exceedances were likely related to background air quality level but not project-related.
No breach of the Action or Limit Levels in relation to the construction noise and waste monitoirng were recorded during the reporting period.
Implementation Status and Review of Environmental Mitigation Measures
Weekly site audits were carried out during the reporting period to confirm the implementation measures undertaken by the Contractors. Environmental issues related to the construction activities, including air quality, noise, waste, ecology and landscape & visual were monitored and/or reviewed.
The recommended environmental mitigation measures, as included in the EM&A programme, were implemented properly in the reporting period. The EM&A programme effectively monitored the construction activities and ensure the proper implementation of mitigation measures.
Summary findings of the EM&A programme
The following table summarizes the key findings of the EM&A programme during the reporting period:
|
Yes |
No |
Details |
Analysis / Recommendation / Remedial Actions |
Breaches of Limit Level^ |
|
ü |
No exceedance of project-related limit level was recorded. |
Nil |
Breaches of Action Level^
|
|
ü |
No exceedance of project-related action level was recorded. |
Nil |
Complaints Received |
|
ü |
No construction activities related complaints were received. |
Nil |
Notification of any summons and status of prosecutions |
|
ü |
Neither notifications of summons nor prosecution were received. |
Nil |
Changes that affect the EM&A |
|
ü |
There were no changes to the construction works that may affect the EM&A |
Nil |
Remarks: ^ only exceedance of action/ limit level related to Project works will be highlighted.
On 7 November 2014, the Environmental Impact Assessment (EIA) Report (Register No.: AEIAR-185/2014) for the “Expansion of Hong Kong International Airport into a Three-Runway System” (the Project) was approved and an Environmental Permit (EP) (Permit No.: EP-489/2014) was issued for the construction and operation of the Project.
Airport Authority Hong Kong (AAHK) commissioned Mott MacDonald Hong Kong Limited (MMHK) to undertake the role of Environmental Team (ET) for carrying out the Environmental Monitoring & Audit (EM&A) works during the construction phase of the Project in accordance with the Updated EM&A Manual (the Manual) submitted under EP Condition 3.1. The Manual is available on the Project’s dedicated website (accessible at: http://env.threerunwaysystem.com/en/index.html). AECOM Asia Company Limited (AECOM) was employed by AAHK as the Independent Environmental Checker (IEC) for the Project.
The Project covers the expansion of the existing airport into a three-runway system (3RS) with key project components comprising land formation of about 650 ha and all associated facilities and infrastructure including taxiways, aprons, aircraft stands, a passenger concourse, an expanded Terminal 2, all related airside and landside works and associated ancillary and supporting facilities. The existing submarine aviation fuel pipelines and submarine power cables also require diversion as part of the works.
Construction of the Project is to proceed in the general order of diversion of the submarine aviation fuel pipelines, diversion of the submarine power cables, land formation, and construction of infrastructure, followed by construction of superstructures.
The commencement of initial reclamation works was announced on 1 August 2016. The updated overall phasing programme of all construction works and the contract information are provided in Appendix A.
This is the 3rd Construction Phase Quarterly EM&A Report for the Project which summarizes the key findings of the EM&A programme during the reporting period from 1 July 2016 to 30 September 2016.
The Project’s organisation structure and the contact details of the key personnel are provided in Appendix B and Table 1.1 respectively.
Table 1.1: Contact Information of Key Personnel
Party |
Position |
Name |
Telephone |
Project Manager’s Representative (Airport Authority Hong Kong) |
Senior Manager, Environment |
Lawrence Tsui |
2183 2734 |
Environmental Team (ET) (Mott MacDonald Hong Kong Limited) |
Environmental Team Leader |
Terence Kong |
2828 5919 |
|
Deputy Environmental Team Leader |
Heidi Yu |
2828 5704 |
|
Deputy Environmental Team Leader |
Keith Chau |
2972 1721 |
Independent Environmental Checker (IEC) (AECOM Asia Company Limited) |
Independent Environmental Checker |
Jackel Law |
3922 9376
|
|
Deputy Independent Environmental Checker |
Joanne Tsoi |
3922 9423 |
Advanced Works Contract: |
|
|
|
Contract P560(R) Aviation Fuel Pipeline Diversion Works (Langfang Huayuan Mechanical and Electrical Engineering Co., Ltd.) |
Project Manager
|
Shih Wei
|
2117 0566
|
Environmental Officer |
Lyn Lau
|
5172 6543
|
|
DCM Works Contracts: |
|
|
|
Contract 3201 DCM (Package 1) (Penta-Ocean-China State-Dong-Ah Joint Venture) |
Project Director
|
Mr. Tsugunari SUZUKI
|
9178 9689 |
|
Environmental Officer
|
Mr. Kanny CHO
|
9019 1962 |
Contract 3202 DCM (Package 2) (Samsung-BuildKing Joint Venture) |
Project Manager
|
Mr. Ilkwon Nam
|
9643 3117 |
|
Environmental Officer
|
Mr. Dickson Mak
|
9525 8408 |
Contract 3203 DCM (Package 3) (Sambo E&C Co.,Ltd) |
Project Manager
|
Mr. Park Seong Jae
|
9683 8693 |
|
Environmental Officer
|
Mr. Leung Min Pong
|
9203 5820 |
Contract 3204 DCM (Package 4) (CRBC-SAMBO Joint Venture) |
Project Manager
|
Mr. Yoo Kyung-Sik
|
9683 8697
|
|
Environmental Officer
|
Mr. David Man |
6421 3238 |
Other Works contract: |
|
|
|
Contract 3213 CLP Cable Diversion Enabling Works (Wing Hing Construction Company)
|
Environmental Officer
|
Mr. Kan Yun Tai, Michael |
9206 0550 |
|
Environmental Officer |
Ms Ivy Tam |
2151 2090 |
The contact information for the Project is provided in Table 1.2. The public can contact us through the following channels if they have any queries and comments on the environmental monitoring data and project related information.
Table 1.2: Contact Information of the Project
Channels |
Contact Information |
Hotline |
3908 0354 |
|
|
Fax |
3747 6050 |
Postal Address |
Airport Authority Hong Kong HKIA Tower 1 Sky Plaza Road Hong Kong International Airport Lantau Hong Kong Attn: Environmental Team Leader Mr Terence Kong c/o Mr Lawrence Tsui (TRD) |
During the reporting period, no marine construction work was carried out. Key activities of the Project were related to the Contract P560(R) Aviation Fuel Pipeline Diversion Works (Contract P560(R)) which involved installation of HDD casing and pilot hole drilling at the HDD launching site located at the west part of the airport, stockpiling of excavated materials from HDD operation at stockpiling area, site preparation works and construction of containment pit at Sheung Sha Chau. CLP cable diversion enabling work contract involved site preparation works. The four DCM contracts involved mobilization and off-site plant fabrication. There are also some site investigation works conducted during the reporting period.
The locations of the works areas are presented in Figure 1.1 to Figure 1.2. Some site investigation works were carried out during the reporting period.
As presented in the Updated EM&A Manual, the environmental aspects of interest for the Project include air quality, noise, water quality, waste management, land contamination, terrestrial ecology, marine ecology, fisheries, landscape and visual, sewage and sewerage, and hazard to human life.
The status for all environmental aspects is presented in Appendix A.
Table 1.3: Summary of Status for All Environmental Aspects under the Updated EM&A Manual
Parameters |
|
|
Status |
||
Air Quality |
|
|
|
||
Baseline Monitoring |
At least 14 consecutive days before commencement of construction work |
|
The baseline air quality monitoring result has been reported in Baseline Monitoring Report (Version 1) and submitted to EPD under EP Condition 3.4. |
||
Impact Monitoring |
At least 3 times every 6 days |
|
On-going |
||
Noise |
|
|
|
||
Baseline Monitoring |
Daily for a period of at least two weeks prior to the commencement of construction works |
|
The baseline noise monitoring result has been reported in Baseline Monitoring Report (Version 1) and submitted to EPD under EP Condition 3.4. |
||
Impact Monitoring |
Weekly |
|
On-going |
||
Water Quality |
|
|
|
||
General Baseline Water Quality Monitoring for reclamation, water jetting and field joint works |
Three days per week, at mid-flood and mid-ebb tides, for at least four weeks prior to the commencement of marine works. |
|
The baseline water quality monitoring result has been reported in Water Quality Baseline Monitoring Report and submitted to EPD under EP Condition 3.4. |
||
General Impact Water Quality Monitoring for reclamation, water jetting and field joint works |
Three days per week, at mid-flood and mid-ebb tides. |
|
The general water quality monitoring were completed as scheduled in August and September 2016 , although there were no marine construction works. |
||
Initial Intensive Deep Cement Mixing (DCM) Water Quality Monitoring |
At least four weeks |
|
To be commenced according to the detailed plan on DCM |
||
Regular DCM Water Quality Monitoring |
Three times per week until completion of DCM works. |
|
The early regular DCM water quality monitoring were completed as scheduled in August and September 2016, although there were no marine construction works. |
||
Waste Management |
|
|
|
||
Waste Monitoring |
At least weekly |
|
On-going |
||
Land Contamination |
|
|
|
||
Supplementary Contamination Assessment Plan (CAP) |
At least 3 months before commencement of any soil remediation works. |
|
To be submitted with the relevant construction works |
||
Contamination Assessment Report (CAR) for Golf Course |
CAR to be submitted for golf course first; programme for submission of supplementary CAR at the other areas to be agreed. |
|
The CAR for Golf Course was submitted to EPD. |
||
Terrestrial Ecology |
|
|
|
||
Pre-construction Egretry Survey Egretry Survey Plan |
Once per month in the breeding season between April and July, prior to the commencement of HDD drilling works. |
|
The revised Egretry Survey Plan was submitted and approved by EPD under EP Condition 2.14. |
||
Ecological Monitoring |
Monthly monitoring during the HDD construction works period from August to March. |
|
No construction work was carried out on Sheung Sha Chau Island during the ardeid’s breeding season in July 2016 in accordance with the Updated EM&A Manual. Ecological monitoring was commenced in August 2016. |
||
Marine Ecology |
|
|
|
||
Pre-Construction Phase Coral Dive Survey |
Prior to marine construction works |
|
The Coral Translocation Plan was submitted and approved by EPD under EP Condition 2.12. |
||
Coral Translocation |
- |
|
On-going |
||
Chinese White Dolphins (CWD) |
|
|
|||
|
|
||||
Baseline Monitoring |
6 months of baseline surveys before the commencement of land formation related construction works at a frequency of two full surveys per month. |
|
Baseline CWD results were reported in the CWD Baseline Monitoring Report and submitted to EPD in accordance with EP Condition 3.4. |
||
Impact Monitoring |
Vessel surveys: Two full surveys per month; Land-based theodolite tracking: One day per month at the Sha Chau station and one day per month at the Lung Kwu Chau Station; and PAM: For the whole duration for land formation related construction works. |
|
Monitoring of CWDs were completed as scheduled in August and September 2016 although there were no marine construction works. |
||
Landscape and Visual |
|
|
|
||
Baseline Monitoring |
One-off survey within the Project site boundary prior to commencement of any construction works |
|
The baseline landscape & visual monitoring result has been reported in Baseline Monitoring Report (Version 1) and submitted to EPD under EP Condition 3.4. |
||
Impact Monitoring |
Weekly |
|
On-going |
||
Environmental Auditing |
|
|
|
||
Regular site inspection |
Weekly |
|
On-going |
||
Skypier High Speed Ferries (HSF) implementation measures |
Monitor and check |
|
On-going |
||
Construction and Associated Vessels Implementation measures |
Monitor and check |
|
The auditing of construction and associated vessels was commenced in August 2016. |
||
Complaint Hotline and Email channel |
Construction phase |
|
On-going |
||
Environmental Log Book |
Construction phase |
|
On-going |
||
Taking into account the construction works in the reporting period, impact monitoring of air quality, noise, waste management and landscape & visual were carried out in the reporting period. Ecological monitoring, water quality monitoring and CWD monitoring were commenced in August 2016 .
The EM&A programme also involved weekly site inspections and related auditings conducted by the ET for checking the implementation of the required environmental mitigation measures recommended in the approved EIA Report.
The EM&A programme followed the recommendations presented in the approved EIA Report and the Updated EM&A Manual. A summary of implementation status of the environmental mitigation measures for the construction phase of the Project during the reporting period is provided in Appendix C.
Impact 1-hour Total Suspended Particulates (TSP) monitoring was conducted three times every 6 days at two representative monitoring stations during the reporting period. The locations of monitoring stations are described in Table 2.1 and presented in Figure 2.1. The Action and Limit Levels of the air quality monitoring are also provided in Table 2.1 for reference.
Table 2.1: Impact Air Quality Monitoring Stations
Monitoring Station |
Location |
Action Level (mg/m3) |
Limit Level (mg/m3) |
AR1A |
Man Tung Road Park |
306 |
500 |
AR2 |
Village House at Tin Sum |
298 |
The graphical plots of impact air quality monitoring results during the reporting period are presented in Graph 1.
Graph 1: Graphical Plot of 1-hour TSP concentration at AR1A and AR2 during the Reporting Period
Three exceedance cases of action level of air quality monitoring were recorded at AR1A on 27 September 2016 in the 1-hour TSP monitoring that started at 08:52am, 09:52am and 10:52am. Actions were taken accordingly based on the established Event and Action Plan as presented in the Updated EM&A Manual. IEC and AAHK were informed of the exceedances.
According to on-site observation by monitoring team, haze weather was observed during monitoring. No major construction dust emission source was observed during monitoring. Based on the information from Hong Kong Observatory, tropical cyclone Megi was approaching Taiwan, its subsidence airstream create unfavourable conditions for the dispersion of pollutants and lead to low visibility to Hong Kong. According to EPD’s pollutant concentration summary at Tung Chung from 08:00 to 12:00 on 27 September 2016, relatively high PM10 ranging from 104 -159 µg/m3 was recorded.
Relevant contractors were informed of the exceedances. As informed by the contractors, no major dusty activities were conducted during monitoring. The major land works were related to P560(R) HDD pilot hole drill, stockpiling of excavated materials and site preparation works at Sha Chau.
The exceedances of 1-hr TSP may possibly due to the air quality impact induced by tropical cyclone Megi. As no major project-related dusty construction work was conducted during monitoring, the exceedance was considered not due to 3RS project construction works and therefore, no repeat measurement is required.
No exceedance of the Action and Limit Level was recorded at AR2 in the reporting period.
The weather was varied from fine to rainy in the reporting quarter. Wind direction was mainly northeast or northwest in the reporting quarter.
Key activities of the Project were related to the Contract P560(R) which mainly involved installation of HDD casing and pilot hole drilling at the HDD launching site, stockpiling of excavated materials from HDD operation at stockpiling area, site preparation works and construction of containment pit on Sheung Sha Chau. CLP cable diversion enabling work contract involved site preparation works. The four DCM contracts involved mobilization and off-site plant fabrication. Those works were not likely to cause adverse dust pollution. The active construction works of Contract P560(R) were around 3 km and 900 m away respectively from the nearest monitoring stations in Tung Chung and the villages in North Lantau. The major dust sources during the reporting period were observed to be local air pollution and nearby traffic emissions. It is considered that the monitoring work in the reporting period was effective and there was no adverse impact attributable to the works of the Project.
Impact noise monitoring was conducted at five representative monitoring stations once per week during 0700 and 1900 during the reporting period. The locations of monitoring stations are described in Table 2.2 and presented in Figure 2.1. The Action and Limit Levels of the noise monitoring are provided in Table 2.2 for reference.
The graphical plots of impact noise quality monitoring results during the reporting period are presented in Graph 2.
Table 2.2: Impact Noise Quality Monitoring Stations
Monitoring Station |
Location |
Action Level |
Limit Level |
NM1A |
Man Tung Road Park |
When one documented complaint is received from any one of the sensitive receivers |
75 dB(A) |
NM3A |
Site Office |
75 dB(A) |
|
NM4(i) |
Ching Chung Hau Po Woon Primary School |
65dB(A) / 70 dB(A) |
|
NM5 |
Village House in Tin Sum |
75 dB(A) |
|
NM6 |
House No. 1, Sha Lo Wan |
75 dB(A) |
|
Note: (i) reduce to 70dB(A) for school and 65dB(A) during school examination periods. |
Graph 2: Graphical Plot of Leq (30min) at NM1A, NM3A, NM4, NM5 and NM6 during the Reporting Period
No exceedance of the Action and Limit Level was recorded at all monitoring stations in the reporting period.
The key activities undertaken in the reporting period were not likely to cause adverse noise impact. The active construction works of Contract P560(R) were around 3 km and 900 m away respectively from the nearest monitoring stations in Tung Chung and the villages in North Lantau. The monitoring stations were observed during the construction noise impact monitoring dominated by aircraft noise at NM3A and NM5, aircraft noise and helicopter noise at NM6, road traffic noise at NM1A and school activities at NM4 in the background. It is considered that the monitoring work in the reporting period was effective and there was no adverse impact attributable to the works of the Project.
Although no marine construction works was carried out, water quality monitoring was commenced as scheduled. The monitoring was conducted at a total of 22 water quality monitoring stations, comprising 12 impact stations, seven sensitive receiver stations and three control stations in the vicinity of the water quality sensitive receviers around the airport island in accordance with the Updated EM&A Manual. Table 2.3 describes the details of the monitoring stations. Figure 2.2 shows the locations of the monitoring stations.
Table 2.3: Monitoring Locations and Parameters for Impact Water Quality Monitoring
Monitoring Stations |
|
Coordinates |
|
|
Description |
Easting |
Northing |
Parameters |
|
C1 |
Control |
804247 |
815620 |
|
C2 |
Control |
806945 |
825682 |
|
C3(3) |
Control |
817803 |
822109 |
|
IM1 |
Impact |
806458 |
818351 |
DO, pH, Temperature, Salinity, Turbidity, SS, Total Alkalinity, Heavy Metals(2) |
IM2 |
Impact |
806193 |
818852 |
|
IM3 |
Impact |
806019 |
819411 |
|
IM4 |
Impact |
805039 |
819570 |
|
IM5 |
Impact |
804924 |
820564 |
|
IM6 |
Impact |
805828 |
821060 |
|
IM7 |
Impact |
806835 |
821349 |
|
IM8 |
Impact |
807838 |
821695 |
|
IM9 |
Impact |
808811 |
822094 |
|
IM10 |
Impact |
809838 |
822240 |
|
IM11 |
Impact |
810545 |
821501 |
|
IM12 |
Impact |
811519 |
821162 |
|
SR1(1) |
Future Hong Kong-Zhuhai-Macao Bridge Hong Kong Boundary Crossing Facilities (HKBCF) Seawater Intake for cooling |
812586 |
820069 |
DO, pH, Temperature, Salinity, Turbidity, SS
|
SR2(3) |
Planned marine park / hard corals at The Brothers / Tai Mo To |
814166 |
821463 |
|
SR3 |
Sha Chau and Lung Kwu Chau Marine Park / fishing and spawning grounds in North Lantau |
807571 |
822147 |
|
SR4A |
Sha Lo Wan |
807810 |
817189 |
|
SR5A |
San Tau Beach SSSI |
810696 |
816593 |
|
SR6 |
Tai Ho Bay, Near Tai Ho Stream SSSI |
814663 |
817899 |
|
SR7 |
Ma Wan Fish Culture Zone (FCZ) |
823742 |
823636 |
|
SR8 |
Seawater Intake for cooling at Hong Kong International Airport (East) |
811593 |
820417 |
Notes:
(1) the seawater intakes of SR1 for the future HKBCF are not
yet in operation, the future permanent location for SR1
during impact monitoring is subject to finalisation after the HKBCF
seawater is commissioned.
(2)
according to the Baseline Water Quality Monitoring Report, Chromium and Nickel
are the representative heavy metals for early regular DCM monitoring. DCM
specific water quality monitoring parameters (total alkalinity and heavy
metals) were only conducted at C1 to C3, IM1 to IM12 .
(3) according to the baseline water quality monitoring
report, C3 station is not adequately representative as a control
station of impact/ SR stations during the flood tide. The control
reference has been changed from C3 to SR2 from 1 September 2016
onwards.
The Action and Limit Levels levels for general water quality monitoring and regular DCM monitoring are presented in Table 2.4. The control and impact stations during flood tide and ebb tide for general water quality monitoring and regular DCM monitoring are presented in Table 2.5.
Table 2.4: Action and Limit Levels for General Water Quality Monitoring and Regular DCM Monitoring
Parameters |
Action Level (AL) |
Limit Level (LL) |
||
Action and Limit Levels for general water quality monitoring and regular DCM monitoring (excluding SR1& SR8) |
||||
DO in mg/L (Surface, Middle & Bottom) |
Surface and Middle 4.8 mg/L |
Surface and Middle 4.1 mg/L 5 mg/L for Fish Culture Zone (SR7) only |
||
Bottom 3.1 mg/L |
Bottom 2.3 mg/L |
|||
Suspended Solids (SS) in mg/L |
25 |
or 120% of upstream control station at the same tide of the same day, whichever is higher |
36 |
or 130% of upstream control station at the same tide of the same day, whichever is higher |
Turbidity in NTU |
26.0 |
41.4 |
||
Total Alkalinity in ppm |
95 |
98 |
||
Representative Heavy Metals for early regular DCM monitoring (Chromium) |
0.2 |
0.2 |
||
Representative Heavy Metals for early regular DCM monitoring (Nickel) |
3.2 |
|
3.4 |
|
Action and Limit Levels SR1 |
|
|
|
|
SS (mg/l) |
To be determined prior to its commissioning |
To be determined prior to its commissioning |
||
Action and Limit Levels SR8 |
|
|
|
|
SS (mg/l) |
52 |
|
60 |
|
Note:
1. For DO measurement, non-compliance occurs when monitoring result is lower than the limits.
2. For parameters other than DO, non-compliance of water quality results when monitoring results is higher than the limits.
3. Depth-averaged results are used unless specified otherwise.
4. Details of selection criteria for the two heavy metals for early regular DCM monitoring refer to the Detailed Plan on Deep Cement Mixing available on the dedicated 3RS website http://env.threerunwaysystem.com/en/ep-submissions.html)
5. The action and limit levels for the two representative heavy metals chosen will be the same as that for the intensive DCM monitoring.
Table 2.5: The Control and Impact Stations during Flood Tide and Ebb Tide for General Water Quality Monitoring and Regular DCM Monitoring
Control Station |
Impact Stations |
Flood Tide |
|
C1 |
IM1, IM2, IM3, IM4, IM5, IM6, IM7, IM8, SR3 |
SR2^1 |
IM7, IM8, IM9, IM10, IM11, IM12, SR1A, SR3, SR4A, SR5A, SR6, SR8 |
Ebb Tide |
|
C1 |
SR4A, SR5A, SR6 |
C2 |
IM1, IM2, IM3, IM4, IM5, IM6, IM7, IM8, IM9, IM10, IM11, IM12, SR1A, SR2, SR3, SR7, SR8 |
^1 As per findings of Baseline Water Quality Report, the control reference has been changed from C3 to SR2 from 1 Sep 2016 onwards.
Water quality monitoring was commenced in August 2016. No marine construction works were conducted in August and September 2016, and hence no adverse water quality impact arised from the project was observed. The general water quality monitoring was completed as scheduled. The graphical plots of water quality monitoring results during the reporting period are presented in Appendix D.
In accordance with the Updated EM&A Manual, the waste generated from construction activities was audited once per week to determine if wastes were being managed in accordance with the Waste Management Plan (WMP) prepared for the Project, contract-specific WMP, and any statutory and contractual requirements. All aspects of waste management including waste generation, storage, transportation and disposal were assessed during the audits. The Action and Limit levels of the construction waste are provided in Table 2.6.
Table 2.6: Action and Limit Levels for Construction Waste
Monitoring Stations |
Action Level |
Limit Level |
Construction Area |
When one valid documented complaint is received |
Non-compliance of the WMP, contract-specific WMPs, any statutory and contractual requirements |
Weekly waste monitoring of the Project construction works to check and monitor the implementation of proper waste management practices during the construction phase during the reporting period.
Recommendation was provided for P560(R) Aviation Fuel Pipeline Diversion Works during monitoring including review of the capacity of chemical waste storage, provision of drip tray for the oil drums, proper maintenance of drip tray and removal of oil stain on ground as chemical waste on sites.
Under the P560(R) Contract, about 621 m3 excavated material from the launching site has been delivered and temporarily stored at the stockpiling area at Chun Ming Road adjacent to Tradeport Logistic Centre on the airport island during the reporting period. The excavated material will be reused in the Project, including as backfilling material at the launching site.
In addition, metals and paper were recycled. During the reporting period, 9.3 tonnes of general refuse were disposed of to the West New Territories (WENT) Landfill and no Construction and Demolition (C&D) material was disposed off-site. No exceedances of the Action and Limit Levels of waste monitoring were recorded during the reporting period.
No waste was generated from other contracts during the reporting period.
CWD monitoring was conducted by vessel line-transect survey at a frequency of two full survey per month, supplemented by land-based theodolite tracking for twice per month at the Sha Chau station and three times per month at the Lung Kwu Chau station as well as Passive Acoustic Monitoring. Monitoring was completed in the reporting period, although there were no marine construction works. The locations of CWD monitoring by vessel survey transect are shown in Figure 2.3, whilst the land-based survey stations are described in Table 2.7 and depicted in Figure 2.4. Location of Passive Acoustic Monitoring is shown in Figure 2.10.
Table 2.7: Land-based Survey Station Details
Stations |
Location |
Geographical Coordinates |
Station Height (m) |
Approximate Tracking Distance (km) |
D |
Sha Chau (SC) |
22° 20’ 43.5” N 113° 53’ 24.66” E |
45.66 |
2 |
E |
Lung Kwu Chau (LKC) |
22° 22’ 44.83” N 113° 53’ 0.2” E |
70.40 |
3 |
The Action Level (AL) and Limit Level (LL) for CWD monitoring were formulated by an action response approach using the running quarterly dolphin encounter rates (STG and ANI) derived from baseline monitoring data, as presented in the CWD Baseline Monitoring Report. The derived values of AL and LL for CWD monitoring are shown in Table 2.8.
Table 2.8: Derived Values of Action Level (AL) and Limit Level (LL) for Chinese White Dolphin Monitoring
|
NEL, NWL, AW, WL and SWL as a Whole |
Action Level |
Running quarterly STG < 1.86 & ANI < 9.35 |
Limit Level |
Two consecutive running quarterly (3-month) STG < 1.86 & ANI < 9.35 |
Vessel Line-transect Survey
Survey Effort
During the reporting period, four complete sets of vessel line-transect surveys were conducted from August to September 2016 to cover all transects in NEL, NWL, AW, WL and SWL survey area twice per month.
A total of 939 km of survey effort was collected from these surveys, with around 94.5% of the total survey effort being conducted under favourable weather condition (i.e. Beaufort Sea State 3 or below with favourable visibility). Details of the survey effort data were presented in Appendix E.
Sighting Distribution
In August and September 2016, 37 groups of CWD with 142 individuals were sighted. Amongst the sightings of CWD, 31 groups with 128 individuals were made during on-effort search under favourable weather condition.
Distribution of CWD sightings recorded during August 2016 to September 2016 are illustrated in Figure 2.5. CWD sightings were more frequent in WL than in NWL and SWL. In NWL, sightings were mainly recorded to the northeast and to the southwest of Sha Chau and Lung Kwu Chau Marine Park (SCLKCMP). One sighting was recorded in AW near to the existing Hong Kong International Airport, whilst no sightings of CWDs were recorded within the 3RS land-formation footprint. CWD sightings in WL were evenly distributed in both coastal and off-shore areas from Tai O to Fan Lau. In SWL waters, CWD sightings were frequently sighted along the coast from Fan Lau to Lo Kei Wan, with a few scattered sightings further off-shore. Details of the sighting data were presented in Appendix E.
Figure 2.5: Sightings Distribution of Chinese White Dolphins
[Pink circle: Sighting locations of CWD, White line: Vessel survey transects, Blue polygon: Sha Chau and Lung Kwu Chau Marine Park (SCLKCMP), Red polygon: 3RS land-formation footprint]
Note: Only on-effort sightings under Beaufort 3 or below were presented in the figure.
Encounter Rate
The dolphin encounter rates for the number of dolphin sightings per 100km survey effort (STG) and for the total number of dolphins per 100km survey effort (ANI) in the whole survey area (i.e. NEL, NWL, AW, WL and SWL) for August and September 2016 are summarized in Table 2.9.
Table 2.9: Summary of Monthly and Running Quarterly STG and ANI of Chinese White Dolphin for August and September 2016
|
Encounter Rate (STG) |
Encounter Rate (ANI) |
August 2016 |
3.48 |
14.17 |
Running Quarterly of August 2016 |
4.93 |
20.57 |
September 2016 |
3.50 |
14.65 |
Running Quarterly of September 2016 |
4.29 |
18.32 |
Note: For detailed calculations of encounter rates STG and ANI, please refer to the Monthly EM&A Reports No. 8 and No. 9.
Group Size
In August and September 2016, the group size of CWDs ranged from 1 to 10 individuals per group. The average group size of CWDs was 4.1 individuals per group. The numbers of CWD sightings with small group size (i.e. 1-2 individuals) and medium group size (3-9 individuals) were 12 and 18 respectively. The majority of CWD groups encountered in NWL were of medium group size. In WL, medium-sized CWD groups were mainly sighted along the coast. One large CWD group with 10 individuals was sighted in WL. Sighting locations of CWD groups with different group sizes were depicted in Figure 2.6.
Figure 2.6: Sighting Locations of Chinese White Dolphins with Different Group Sizes
Note: Only on-effort sightings under Beaufort 3 or below were presented in the figure.
Activities and Association with Fishing Boats
During August 2016 and September 2016, 19 groups of CWDs were sighted with feeding activities. Two groups amongst 19 were observed in association with operating purse seiners, one in WL and the other in SWL. In NWL waters, the majority of the feeding activities of CWDs were observed around SCLKCMP, while CWDs manily fed along the coast of WL and SWL during the current reporting months. The sighting locations of CWDs engaged in different behaviours during the current reporting months were illustrated in Figure 2.7.
Figure 2.7: Sighting Locations of Chinese White Dolphins Engaged in Different Behaviours
[Indigo rhombus: Feeding, Green circle: Socializing, Pink square: Resting, Yellow triangle: Travelling, White line: Vessel survey transects, Blue polygon: SCLKCMP, Red polygon: 3RS land-formation footprint]
Mother-calf Pairs
In August 2016, two mother-calf pairs were sighted in WL and one mother-spotted juvenile pair was sighted in NWL near Lung Kwu Chau. No mother-calf or mother-spotted juvenile pairs were sighted in September 2016. The sighting locations of those mother-calf pairs were shown in Figure 2.8.
Figure 2.8: Sighting Locations of Mother-calf Pairs
[Pink circle: Sighting locations of mother-calf pairs, White line: Vessel survey transects, Blue polygon: Sha Chau and Lung Kwu Chau Marine Park (SCLKCMP), Red polygon: 3RS land-formation footprint]
During August 2016 and September 2016, a total number of 52 different CWD individuals sighted altogether 68 times were identified. Amongst these 52 identified individuals, 13 animals (i.e. NLMM002, NLMM006, NLMM010, NLMM013, NLMM028, NLMM038, SLMM002, SLMM010, SLMM011, SLMM015, WLMM027, WLMM043 and WLMM054) were sighted more than once. A summary of photo identification works is presented in Table 2.10. Representative photos of these individuals may refer to Appendix E.
Re-sighting locations of the identified CWD individuals and further detailed analysis of CWD monitoring results collected by vessel survey during construction phase would be included starting from the next Quarterly EM&A Report when there are more data and photos collected.
Table 2.10: Summary of Photo Identification
Individual ID |
Date of sighting |
Sighting Group No. |
Area |
|
Individual ID |
Date of sighting |
Sighting Group No. |
Area |
NLMM002 |
19/08/2016 |
1 |
NWL |
|
SLMM017 |
26/09/2016 |
3 |
SWL |
2 |
NWL |
|
SLMM022 |
19/09/2016 |
2 |
WL |
||
24/08/2016 |
1 |
NWL |
|
4 |
WL |
|||
22/09/2016 |
2 |
NWL |
|
SLMM030 |
19/09/2016 |
4 |
WL |
|
NLMM004 |
19/08/2016 |
2 |
NWL |
|
5 |
WL |
||
NLMM005 |
22/09/2016 |
1 |
NWL |
|
SLMM032 |
19/09/2016 |
6 |
SWL |
2 |
NWL |
|
SLMM034 |
19/09/2016 |
2 |
WL |
||
NLMM006 |
24/08/2016 |
1 |
NWL |
|
SLMM050 |
26/09/2016 |
3 |
SWL |
22/09/2016 |
2 |
NWL |
|
SLMM051 |
26/09/2016 |
3 |
SWL |
|
NLMM008 |
22/08/2016 |
3 |
WL |
|
WLMM007 |
19/09/2016 |
5 |
WL |
NLMM010 |
24/08/2016 |
1 |
NWL |
|
7 |
SWL |
||
06/09/2016 |
1 |
NWL |
|
WLMM013 |
09/08/2016 |
3 |
WL |
|
22/09/2016 |
2 |
NWL |
|
WLMM015 |
19/09/2016 |
5 |
WL |
|
NLMM012 |
08/09/2016 |
2 |
WL |
|
WLMM020 |
19/09/2016 |
7 |
SWL |
NLMM013 |
24/08/2016 |
1 |
NWL |
|
WLMM024 |
19/09/2016 |
1 |
AW |
22/09/2016 |
2 |
NWL |
|
WLMM025 |
19/09/2016 |
2 |
WL |
|
NLMM017 |
08/09/2016 |
2 |
WL |
|
7 |
SWL |
||
NLMM019 |
22/08/2016 |
3 |
WL |
|
WLMM027 |
08/09/2016 |
3 |
WL |
NLMM021 |
27/09/2016 |
6 |
SWL |
|
27/09/2016 |
5 |
SWL |
|
NLMM027 |
22/09/2016 |
2 |
NWL |
|
WLMM030 |
09/08/2016 |
1 |
WL |
NLMM028 |
22/08/2016 |
1 |
WL |
|
WLMM038 |
22/08/2016 |
2 |
WL |
24/08/2016 |
1 |
NWL |
|
WLMM043 |
09/08/2016 |
1 |
WL |
|
22/09/2016 |
2 |
NWL |
|
08/09/2016 |
1 |
WL |
||
NLMM035 |
19/08/2016 |
1 |
NWL |
|
WLMM046 |
09/08/2016 |
3 |
WL |
2 |
NWL |
|
WLMM047 |
22/08/2016 |
2 |
WL |
||
NLMM036 |
19/08/2016 |
1 |
NWL |
|
WLMM048 |
22/08/2016 |
2 |
WL |
NLMM037 |
19/08/2016 |
1 |
NWL |
|
WLMM049 |
22/08/2016 |
4 |
WL |
2 |
NWL |
|
WLMM050 |
08/09/2016 |
2 |
WL |
||
NLMM038 |
22/08/2016 |
1 |
WL |
|
WLMM051 |
08/09/2016 |
2 |
WL |
24/08/2016 |
1 |
NWL |
|
WLMM052 |
08/09/2016 |
2 |
WL |
|
SLMM002 |
19/09/2016 |
2 |
WL |
|
WLMM053 |
08/09/2016 |
2 |
WL |
7 |
SWL |
|
WLMM054 |
08/09/2016 |
3 |
WL |
||
26/09/2016 |
3 |
SWL |
|
27/09/2016 |
5 |
SWL |
||
SLMM010 |
22/08/2016 |
7 |
WL |
|
WLMM055 |
19/09/2016 |
2 |
WL |
19/09/2016 |
7 |
SWL |
|
WLMM056 |
19/09/2016 |
2 |
WL |
|
SLMM011 |
22/08/2016 |
7 |
WL |
|
WLMM057 |
19/09/2016 |
2 |
WL |
25/08/2016 |
1 |
SWL |
|
WLMM058 |
19/09/2016 |
2 |
WL |
|
SLMM015 |
22/08/2016 |
6 |
WL |
|
WLMM059 |
19/09/2016 |
5 |
WL |
7 |
WL |
|
||||||
27/09/2016 |
4 |
SWL |
|
Land-based Theodolite Tracking
Survey Effort
During August 2016 and September 2016, a total of 10 days of land-based theodolite tracking survey effort was completed, including six days on Lung Kwu Chau and four days on Sha Chau. In total, 21 CWD groups were tracked during the surveys. Information on survey effort and CWD groups sighted during these land-based theodolite tracking surveys are presented in Table 2.11. Details on the survey effort and CWD groups tracked are presented in Appendix E. The first sighting locations of CWD groups tracked during land-based theodolite tracking surveys in August 2016 and September 2016 are shown in Figure 2.9.
Table 2.11: Summary of Survey Effort and CWD Group of Land-based Theodolite Tracking
Land-based Station |
# of Survey Sessions |
Survey Effort (hh:mm) |
# CWD Groups Sighted |
CWD Group Sighting per Survey Hour |
August 2016 |
||||
Lung Kwu Chau |
3 |
18:11 |
11 |
0.607 |
Sha Chau |
2 |
12:10 |
1 |
0.083 |
Total |
5 |
30:21 |
12 |
0.395 |
September 2016 |
||||
Lung Kwu Chau |
3 |
18:00 |
9 |
0.5 |
Sha Chau |
2 |
12:00 |
0 |
0 |
Total |
5 |
30:00 |
9 |
0.3 |
Figure 2.9: Plots of First Sightings of All CWD Groups from Land-based Stations
[Green triangle: LKC station; Green square: CWD group off LKC; Yellow triangle: SC station; Yellow square: CWD group off SC; Blue line: SCLKCMP boundary; Red line: 3RS land-formation footprint]
Progress Update on Passive Acoustic Monitoring (PAM)
An Ecological Acoustic Recorder (EAR) has been deployed and positioned to the south of Sha Chau Island with 20% duty cycle (Figure 2.10) with data from the EAR intended primarily to supplement the data collected from the land-based theodolite station on Sha Chau. The EAR deployment generally lasts around 4-6 weeks followed by a period of data retrieval for subsequent analysis. As the data analysis takes more than two months after retrieval, PAM results are not available for reporting in this quarterly report. Data transfer / analysis of this batch of PAM data is tentatively scheduled for completion by end of November 2016.
Site inspections of the construction works were carried out on a weekly basis to monitor the implementation of proper environmental pollution control and mitigation measures for the Project. Bi-weekly site inspections were also conducted by the Independent Environmental Checker (IEC). Observations have been recorded in the site inspection checklist and passed to the Contractor together with the appropriate recommended mitigation measures where necessary.
The key observations from site inspection and associated recommendations were related to:
● improvement of efficiency and capacity of wastewater treatment facilities,
● proper maintenance of drip tray;
● provision of wheel washing before leaving the construction site;
● removal of oil stains on ground as chemical waste;
● review of the capacity of chemical waste storage area;
● display of Environmental Permit at site entrance;
● erection of site hoarding;
● provision of sandbags around the gully to prevent surface runoff; and
● improvement of dust mitigation measures.
In addition, CNP compliance check of the use of powered mechanical equipment for Contract P560(R) during restricted hour at the launching site was carried out by the ET on 11 July 2016. The use of powered mechanical equipment was complied with the requirements of CNP.
A summary of implementation status of the environmental mitigation measures for the construction phase of the Project during the reporting period is provided in Appendix C.
In accordance with the Updated EM&A Manual, ecological monitoring shall be undertaken monthly at the HDD daylighting location on Sheung Sha Chau Island to identify and evaluate any impacts with appropriate actions taken as required to address and minimise any adverse impact found.
Monthly ecological monitoring was carried out in August and September 2016 on Sheung Sha Chau Island. No encroachment or disturbance to the egretry area at Sheung Sha Chau was recorded during ecological monitoring.
In total, 2,459 ferry movements between HKIA SkyPier and Zhuhai / Macau were audited in the reporting period. The daily movements of all SkyPier HSFs in the reporting period ranged between 10 and 95, which falls within the maximum daily cap number of 125. There are fewer ferry movements on 1st and 2nd August 2016 (52 and 10 movements respectively) due to typhoon. Status of compliance with annual daily average of 99 movements will be further reviewed in the annual EM&A Report.
All the HSFs had travelled through the SCZ with prevailing speed within 15 knots (7.8 knots to 14.8 knots), which complied with the SkyPier Plan. 15 ferry movements had minor deviations from the diverted route during the reporting period. Notices were sent to the ferry operators and the cases have been investigated. In July, six cases recorded with the same ferry were not related to public safety / emergency situations. Warning letter has been issued to the concerned ferry operator to prevent reoccurrence. The ferry operator was requested to check the coordinates of SCZ plotted on the radar. Refresher training to the two concerned vessel captains was provided by experienced captain of the concerned ferry operator to ensure the captains are familiarised with the SkyPier Plan requirements. In August, one case was not related to public safety / emergency situations. Investigation found that the SCZ was plotted inaccurately in the radar graph and it was the first time the HSF used the diverted route. The ferry operator had checked and corrected the coordinates of SCZ in both the radar graph and electronic marine chart. The remaining eight cases are related to public safety / emergency situations. The summary of the Skypier Plan monitoring result (June to September 2016) is presented in Graph 3.
Two HSF movements with no transmission of AIS data received were reported during the reporting period. After investigation, it was found that missing of AIS data for concerned ferries were due to interference effect of AIS signal. Vessel captains were requested to provide the radar track photos which indicated the vessel entered the SCZ though the gate access point and no speeding in the SCZ. Ferry operator’s explanation has been accepted.
Graph 3: Summary of SkyPier Plan Monitoring Results (June to September 2016)
The audit of construction and associated vessels has been started in August. ET has conducted weekly audit of relevant information including AIS data, vessel tracks and other relevant records to ensure sufficient information has been provided by the contractors to the Marine Traffic Control Center (MTCC) and the contractors are complied with the requirements of the MTRMP-CAV. The contactors have been reminded to submit the endorsed vessel 3-month programme to MTCC for the review of keeping the number of construction vessels to a practicable minimum. The IEC has also performed audit on the compliance of the requirements as part of the EM&A programme.
A total of 11 skipper training workshops have been held in August and September with concerned captains of construction vessels associated with Contract P560(R) Aviation Fuel Pipeline Diversion Works and the four DCM contracts to familiarise them with the predefined routes, general education on local cetaceans, guidelines for avoiding adverse water quality impact, the required environmental practices / measures while operating construction and associated vessels under the Project, and guidelines for operating vessels safely in the presence of CWDs. Trainings have also been held in September with the 4 DCM and P560(R) contractor senior management staff to strengthen the communication between senior management and the sub-contractor and facilitating them in familiarise with the requirements of the MTRMP-CAV. In addition, a Marine Management Liaison Group (MMLG) has been set up and provided a forum to assist and resolve any marine issues which may be encountered under 3RS project. The 2nd MMLG meeting was held on 26 September 2016.
With reference to Appendix E of the Updated EM&A Manual, it is noted that the key assumptions adopted in approved EIA report for the construction phase are still valid and no major changes are involved. The environmental mitigation measures recommended in the approved EIA Report remain applicable and shall be implemented in undertaking construction works for the Project.
Cumulative statistics on exceedance, non-compliance, complaints, notifications of summons and status of prosecutions are summarized in Table 3.1 and Table 3.2.
Table 3.1: Statistics for Valid Exceedances for the Environmental Monitoring
|
|
Total no. recorded in the reporting period |
Total no. recorded since the project commenced |
|
1-hr TSP |
|
Action |
0 |
0 |
|
|
Limit |
0 |
0 |
Noise |
|
Action |
0 |
0 |
|
|
Limit |
0 |
0 |
Waste |
|
Action |
0 |
0 |
|
|
Limit |
0 |
0 |
Remark: Exceedances, which are not project related, are not shown in this table.
Table 3.2: Statistics for Non-compliance, Complaints, Notifications of Summons and Prosecution
Reporting Period |
Cumulative Statistics |
|||
|
Non-compliance |
Complaints |
Notifications of Summons |
Prosecutions |
This reporting period |
0 |
0 |
0 |
0 |
From 28 December 2015 to end of the reporting period |
0 |
0 |
0 |
0 |
In this quarterly period from 1 July 2016 to 30 September 2016, the EM&A programme has been implemented as planned, including 99 sets of air quality measurements, 65 sets of construction noise measurements, two ecological monitoring on Sheung Sha Chau Island, as well as environmental site inspections, landscape & visual and waste monitoring for the Project’s construction works.
Twenty-five sets of water quality measurements, four complete sets of vessel line-transect surveys and ten days of land-based theodolite tracking survey effort for Chinese White Dolphin (CWD) monitoring were completed as scheduled although no marine construction works was carried out during the reporting period.
Key activities of the Project carried out in the reporting period were related to Contract P560(R) which involved installation of HDD casing and drilling of HDD pilot hole at launching site, stockpiling of excavated materials from HDD operation at stockpiling area, site preparation works and construction of containment pit at Sheung Sha Chau. Works under the four DCM contracts involved mobilization and off-site plant fabrication, and CLP cable diversion enabling work involved site preparation works. Some other site investigation works were also carried out during the reporting period.
Three exceedance cases involving Action Level of 1-hour TSP monitoring were recorded during the reporting period. The investigation results indicated that the exceedances were likely related to background air quality level but not project-related.
No breach of the Action or Limit Levels in relation to the construction noise and waste monitoring were recorded in the reporting month. All site observations made by the ET were recorded in the site inspection checklists and passed to the Contractor together with the recommended follow-up actions. No encroachment or disturbance to the egretry area on Sheung Sha Chau was recorded during monthly ecological monitoring.
In total, 2,459 ferry movements between HKIA SkyPier and Zhuhai / Macau were audited in the reporting period. All the HSFs had travelled through the SCZ with prevailing speed within 15 knots, which complied with the SkyPier Plan. Fifteen ferry movements had minor deviation from the diverted route during the reporting period. Among the 15 cases, eight cases are related to public safety / emergency situations. Follow-up actions such as checking of electronic marine chart / radar graphs and refresher training have been taken for the remaining non-public safety / emergency cases.
The audit of construction and associate vessels has been started in August. ET has conducted weekly audit of relevant information to ensure sufficient information has been provided by the contractors to the Marine Traffic Control Center (MTCC) and the contractors are fully complied with the requirements of the MTRMP-CAV. A total of 11 skipper training workshops have been held in August and September with concerned captains of construction vessels associated with Contract P560(R) Aviation Fuel Pipeline Diversion Works and the four DCM contracts to familiarise them with the MTRMP-CAV.
The recommended environmental mitigation measures, as included in the EM&A programme, have been effectively implemented during the reporting period. Also, the EM&A programme implemented by the ET has effectively monitored the construction activities and ensure the proper implementation of mitigation measures.