Expansion of Hong Kong International Airport into a Three-Runway System |
Construction Phase Monthly EM&A Report No.67 (For July 2021) |
Contents
3RS |
Three-Runway System |
AAHK |
Airport Authority Hong Kong |
AECOM |
AECOM Asia Company Limited |
AFCD |
Agriculture, Fisheries and Conservation Department |
AIS |
Automatic Information System |
ANI |
Encounter Rate of Number of Dolphins |
APM |
Automated People Mover |
AW |
Airport West |
BHS |
Baggage Handling System |
C&D |
Construction and Demolition |
CAP |
Contamination Assessment Plan |
CAR |
Contamination Assessment Report |
CTCC |
Construction Traffic Control Centre |
CWD |
Chinese White Dolphin |
DCM |
Deep Cement Mixing |
DEZ |
Dolphin Exclusion Zone |
DO |
Dissolved Oxygen |
EIA |
Environmental Impact Assessment |
EM&A |
Environmental Monitoring & Audit |
EP |
Environmental Permit |
EPD |
Environmental Protection Department |
EPSS |
Emergency Power Supply Systems |
ET |
Environmental Team |
FCZ |
Fish Culture Zone |
HKBCF |
Hong Kong-Zhuhai-Macao Bridge Hong Kong Boundary Crossing Facilities |
HKIA |
Hong Kong International Airport |
HOKLAS |
Hong Kong Laboratory Accreditation Scheme |
HSF |
High Speed Ferry |
HVS |
High Volume Sampler |
IEC |
Independent Environmental Checker |
LKC |
Lung Kwu Chau |
MMHK |
Mott MacDonald Hong Kong Limited |
MMWP |
Marine Mammal Watching Plan |
MSS |
Maritime Surveillance System |
MTRMP-CAV |
Marine Travel Routes and Management Plan for Construction and Associated Vessel |
NEL |
Northeast Lantau |
NWL |
Northwest Lantau |
PAM |
Passive Acoustic Monitoring |
PM |
Project Manager |
SC |
Sha Chau |
SCZ |
Speed Control Zone |
SCLKCMP |
Sha Chau and Lung Kwu Chau Marine Park |
SS |
Suspended Solids |
SSSI |
Site of Special Scientific Interest |
STG |
Encounter Rate of Number of Dolphin Sightings |
SWL |
Southwest Lantau |
T2 |
Terminal 2 |
The Project |
The Expansion of Hong Kong International Airport into a Three-Runway System |
The SkyPier Plan |
Marine Travel Routes and Management Plan for High Speed Ferries of SkyPier |
The Manual |
The Updated EM&A Manual |
TSP |
Total Suspended Particulates |
WL |
West Lantau |
WMP |
Waste Management Plan |
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 Manual).
This is the 67th Construction Phase
Monthly EM&A Report for the Project which summarises the monitoring results
and audit findings of the EM&A programme during the reporting period from 1
to 31 July 2021.
Key Activities in the Reporting Period
The key activities of the Project
carried out in the reporting period included reclamation works and land-based
works. Works in the reclamation areas included marine filling, seawall and
facilities construction, together with runway and associated works such as
bored piling for approach lights. Land-based works on existing airport island
involved mainly airfield works, foundation and substructure work for Terminal 2
expansion, modification and tunnel work for Automated People Mover (APM) and
Baggage Handling System (BHS), and preparation work for utilities, with
activities include site establishment, site office construction, road and
drainage works, cable ducting, demolition, piling, and excavation works.
EM&A
Activities Conducted in the Reporting Period
The monthly EM&A programme was
undertaken in accordance with the Manual of the Project. Summary of the
monitoring activities during this reporting period is presented as below:
Monitoring Activities |
Number of Sessions |
1-hour Total Suspended Particulates (TSP) air quality monitoring |
30 |
Noise monitoring |
18 |
Water quality monitoring |
13 |
Vessel line-transect surveys for Chinese White Dolphin (CWD) monitoring |
2 |
Land-based theodolite tracking survey effort for CWD monitoring |
2 |
Environmental auditing works, including weekly
site inspections of construction works conducted by the ET and bi-weekly site
inspections conducted by the Independent Environmental Checker (IEC), audit of SkyPier High Speed Ferries (HSF), audit of construction and
associated vessels, and audit of implementation of Marine Mammal Watching Plan
(MMWP) and Dolphin Exclusion Zone (DEZ) Plan, were conducted in the reporting
period. Based on information including ET’s observations, records of Maritime
Surveillance System (MSS), and contractors’ site records, it is noted that
environmental pollution control and mitigation measures were properly
implemented and construction activities of the Project in the reporting period
did not introduce adverse impacts to the sensitive receivers.
With reference to the requirement as
stipulated in Section 6.2.1.3 of the Updated EM&A Manual, the proposed methodology
for carrying out the annual sewage flow monitoring for the existing gravity
sewer was approved by EPD on 21 June 2021. The annual sewage flow monitoring
has been started from June 2021.
Snapshots of EM&A Activities in the
Reporting Period
|
|
|
Photo Shoot for Identification of CWD |
Impact Air Quality Monitoring conducted by ET in Man Tung Road Park |
On-site Checking of Water Spraying Record conducted by ET |
Results of Impact Monitoring
The monitoring works for construction dust,
construction noise, water quality, construction waste, landscape
& visual, and CWD were conducted during the reporting period in
accordance with the Manual.
Monitoring results of construction dust,
construction noise, construction waste, and CWD did not trigger the
corresponding Action and Limit Levels in the reporting period.
The water quality monitoring results for all
parameters, except suspended solids (SS), obtained during the reporting period
were within the corresponding Action and Limit Levels stipulated in the
EM&A programme. Relevant investigation and follow-up actions will be
conducted according to the EM&A programme if the corresponding Action and
Limit Levels are triggered. For SS, some of the testing results triggered the
relevant Action or Limit Levels, and the corresponding investigations were
conducted accordingly. The investigation findings revealed that the cases were
not related to the Project. To conclude, the construction activities in the
reporting period did not introduce adverse impact to all water quality
sensitive receivers.
Summary of Upcoming Key Issues
Reclamation Works:
Contract 3206 Main Reclamation Works
● Land-based ground improvement works;
● Seawall construction; and
● Marine filling.
Airfield Works:
Contract 3301 North Runway Crossover Taxiway
● Cable ducting works; and
● Paving works.
Contract 3302 Eastern Vehicular Tunnel Advance Works
● Cable laying and ducting
works;
● Backfilling and
reinstatement works; and
● Piling and structure
works.
Contract 3303 Third Runway and Associated Works
● Footing and utilities
work;
● Piling work;
● Construction of approach
light;
● Operation of asphalt plant; and
● Cable laying and ducting
works.
Contract
3305 Airfield Ground Lighting System
● Genset installation; and
● Site establishment.
Contract 3307 Fire Training Facility
● Architectural, Builder's
and Finishing works;
● Drainage and utilities
works; and
● Building
construction.
Third Runway Concourse:
Contract 3403 New Integrated Airport Centres Building
and Civil Works
● Architectural, Builder's
Work and Finishing works;
● Underground utilities
construction;
● Footing construction;
and
● Sheet piling and
grouting works.
Contract 3405 Third Runway
Concourse Foundation and Substructure Works
● Foundation works;
● Piling work;
● Excavation and
backfilling; and
● Road formation.
Terminal 2 Expansion:
Contract 3503 Terminal 2 Foundation
and Substructure Works
● T2 re-configuration;
● Excavation works;
● Utilities road works; and
● Piling and structure works.
Contract 3508 Terminal 2 Expansion
Works
● Excavation and footing
construction;
● Site formation;
● Piling work; and
● Builders’ works.
Automated People Mover (APM) and Baggage Handling System (BHS):
Contract
3601 New Automated People Mover System (TRC Line)
● Pull out test for
guideway;
● Guidebeam installation; and
● Concreting work.
Contract 3602
Existing APM System Modification Works
● Car modification;
● Formwork erection and;
● Concreting work.
Construction Support
(Facilities):
Contract 3721 Construction Support
Infrastructure Works
● Laying of drainage pipes
and ducts;
● Site clearance;
● Paving works; and
● Road works.
Contract 3722 Construction Support
Facilities
● Electrical and
mechanical installation; and
● Site establishment.
Contract 3723 Construction Support
Facilities
● Erection of site office;
● Electrical and mechanical
installation; and
● Sewage pump and treatment system
installation
Airport Support
Infrastructure:
Contract 3801 APM and BHS Tunnels
on Existing Airport Island
● Formwork and rebar
fixing;
● Backfilling;
● Hanger support
installation; and
● Demolition works.
Contract 3802 APM and BHS Tunnels
and Related Works
● Construction of Airside
Fire Station and marine sediment treatment plant;
● Installation of sheet
pipes and dewatering well;
● Pre-drilling;
● Ground investigation
works; and
● Ducting works.
Construction Support
(Services / Licences):
Contract 3901A Concrete Batching
Facility
● Plant operation; and
● Material conveyor belt
construction.
Contract 3901B Concrete Batching
Facility
● Plant operation; and
● Foundation works for conveyor belt .
Summary
Table
The
following table summarises the key findings of the EM&A programme during
the reporting period:
Yes |
No |
Details |
Analysis / Recommendation / Remedial Actions |
|
Breach of Limit Level^ |
|
√ |
No breach of Limit Level was recorded. |
Nil |
Breach of Action Level^ |
|
√ |
No breach of Action Level was recorded. |
Nil |
Complaint Received
|
√ |
|
In the previous reporting period, a complaint regarding dust issue at the eastern quay of the Project was received on 21 June 2021. |
ET requested the relevant contractors to provide information related to the complaint. Regular site inspections and ad-hoc inspection were conducted in which no observation related to dust issue was recorded. ET also observed contractor was conducting water spraying at concerned area during ET’s site inspection. Nevertheless, all contractors were reminded to continue implementing water spraying properly and adequately at their work areas. ET and IEC would continue to monitor contractors' dust suppression measures during environmental site inspections and the implementation of these measures at the concerned area. Hence, the complaint case was considered closed. |
In the previous reporting period, a complaint regarding muddy water from the Project was received on 28 June 2021. |
ET requested the relevant contractors to provide information related to the complaint. Regular site inspections and joint inspection were conducted in which no illegal discharge was identified in the checklists. Moreover, Hong Kong Observatory issued four Amber Rainstorm Warning Signals on 22, 23, 24 June which might suggest heavy rainfall resulting in surface runoff at the alleged area. To follow up, ET would remind the contractors to pay attention on the possibility of surface run off, especially during rainy season and carry out further improvement on current measures if needed. Hence, the complaint case was considered closed. |
|||
A complaint regarding dust issue at 3RS construction site area was received at 13 July 2021. |
The complaint is under investigation. Findings will be reported in the next Monthly EM&A Report. |
|||
Notification of any summons and status of prosecutions |
|
√ |
No notification of summons or prosecution was received. |
Nil |
Change that affect the EM&A |
|
√ |
There was no change to the construction works that may affect the EM&A. |
Nil |
Note:
^ Only
triggering of Action or Limit Level found related to Project works is counted
as Breach of Action or Limit Level.
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[1].
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 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 summary of construction works programme can
be referred to Section 1.4.
This is the 67th Construction Phase
Monthly EM&A Report for the Project which summarises the key findings of
the EM&A programme during the reporting period from 1 to 31 July 2021.
The Project’s organisation structure presented
in Appendix B of the Construction Phase Monthly EM&A Report No.1 remained
unchanged during the reporting period. Contact details of the key personnel are
presented in Table 1.1.
Table 1.1: Contact Information of Key
Personnel
Party |
Position |
Name |
Telephone |
Project Manager’s Representative (Airport Authority Hong Kong) |
Principal Manager, Environmental Compliance, Sustainability |
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 |
Daniel Sum |
2585 8495 |
|
Independent Environmental Checker (IEC) (AECOM Asia Company Limited) |
Independent Environmental Checker |
Jackel Law |
3922 9376
|
|
Deputy Independent Environmental Checker |
Roy Man |
3922 9141 |
Reclamation Works:
Party |
Position |
Name |
Telephone |
Contract 3206 Main Reclamation Works (ZHEC-CCCC-CDC Joint Venture) |
Project Manager |
Alan Mong |
3763 1352
|
Environmental Officer |
Zhang Bin Wang |
3763 1451 |
Airfield Works:
Party |
Position |
Name |
Telephone |
Contract 3301 North Runway Crossover Taxiway (FJT-CHEC-ZHEC Joint Venture) |
Deputy Project Director |
Kin Hang Chung |
9800 0048 |
Environmental Officer |
Joe Wong |
6182 0351 |
|
Contract 3302 Eastern Vehicular Tunnel Advance Works (China Road and Bridge Corporation) |
Project Manager |
Dickey Yau |
5699 4503 |
Environmental Officer |
Dennis Ho |
5645 0563 |
|
Contract 3303 Third Runway and Associated Works (SAPR Joint Venture) |
Project Manager |
Andrew Keung |
6277 6628 |
Environmental Officer |
Max Chin |
6447 5707 |
|
Contract 3305 Airfield Ground Lighting System (ADB Safegate Hong Kong Limited) |
Project Manager |
Allam Al-Turk |
2944 9725 |
Environmental Officer |
Calvin Sze |
9205 9277 |
|
Contract 3307 Fire Training Facility (Paul Y. Construction Company Limited) |
Project Manager |
Steven Meredith |
6109 1813 |
Environmental Officer |
Albert Chan |
9700 1083 |
Third Runway Concourse:
Party |
Position |
Name |
Telephone |
Contract 3402 New Integrated Airport Centres Enabling Works (Wing Hing Construction Co., Ltd.) |
Contract Manager |
Michael Kan |
9206 0550 |
Environmental Officer |
Lisa He |
5374 3418 |
|
Contract 3403 New Integrated Airport Centres Building and Civil Works (Sun Fook Kong Construction Limited) |
Project Manager |
Alice Leung |
9220 3162 |
Environmental Officer |
Ray Cheung |
9785 1566 |
|
Contract 3405 Third Runway Concourse Foundation and Substructure Works (China Road and Bridge Corporation – Bachy Soletanche Group Limited – LT Sambo Co., Ltd. Joint Venture) |
Project Manager |
Francis Choi |
9423 3469 |
Environmental Officer |
Jacky Lai |
9028 8975 |
|
Contract 3408 Third Runway Concourse and Apron Works (Beijing Urban Construction Group Company Limited and Chevalier (Construction) Company Limited Joint Venture) |
Assistant Project Manager |
Qian Zhang |
5377 7976 |
Environmental Officer |
Malcolm Leung |
7073 7559 |
Terminal 2 (T2) Expansion:
Party |
Position |
Name |
Telephone |
Contract 3503 Terminal 2 Foundation and Substructure Works (Leighton – Chun Wo Joint Venture) |
Project Manager |
Eric Wu |
3973 1718 |
Environmental Officer |
Gomez Yuen |
9098 7807 |
|
Contract 3508 Terminal 2 Expansion Works (Gammon Engineering & Construction Company Limited) |
Project Director |
Richard Ellis |
6201 5637 |
Environmental Officer |
Gena Tsang |
9511 2283 |
Automated People Mover (APM) and
Baggage Handling System (BHS):
Party |
Position |
Name |
Telephone |
Contract 3601 New Automated People Mover System (TRC Line) (CRRC Puzhen Bombardier Transportation Systems Limited and CRRC Nanjing Puzhen Co., Ltd. Joint Venture) |
Project Manager |
Hongdan Wei |
158 6180 9450 |
Environmental Officer
|
P L Wong
|
9143 2185 |
|
Contract 3602 Existing APM System Modification Works (Niigata Transys Co., Ltd.) |
Project Manager |
Kunihiro Tatecho |
9755 0351 |
Environmental Officer |
Carrie Kwan |
9276 0551 |
|
Contract 3603 3RS Baggage Handling System (VISH Consortium) |
Project Manager |
K C Ho |
9272 9626 |
Environmental Officer |
Eric Ha |
9215 3432 |
Construction Support
(Facilities):
Party |
Position |
Name |
Telephone |
Contract 3721 Construction Support Infrastructure Works (China State Construction Engineering (Hong Kong) Ltd.) |
Site Agent |
Thomas Lui |
9011 5340 |
Environmental Officer |
Xavier Lam |
9493 2944 |
|
Contract 3722 Western Support Area – Construction Support Facilities (Tapbo Construction Company Limited and Konwo Modular House Limited Joint Venture) |
Deputy Project Director |
Philip Kong |
9049 3161 |
Environmental Officer |
Eddie Suen
|
6338 8862 |
|
Contract 3723 Eastern Support Area – Construction Support Facilities (Tapbo Construction Company Limited and Konwo Modular House Ltd. Joint Venture.) |
Deputy Project Director |
Philip Kong |
9049 3161 |
Environmental Officer |
Eddie Suen
|
6338 8862 |
|
Contract 3728 Minor Site Works (Shun Yuen Construction Company Limited) |
Contract Manager |
C K Liu |
9194 8739 |
Environmental Officer |
K F Li |
9086 1793 |
Airport Support Infrastructure:
Party |
Position |
Name |
Telephone |
Contract 3801 APM and BHS Tunnels on Existing Airport Island (China State Construction Engineering (Hong Kong) Ltd.) |
Project Manager |
Kingsley Chiang |
9424 8437 |
Environmental Officer |
Ivan Law |
9852 5591 |
|
Contract 3802 APM and BHS Tunnels and Related Works (Gammon Construction Limited) |
Project Director |
John Adams |
6111 6989 |
Environmental Officer |
Phoebe Ng |
9869 1105 |
Construction Support (Services / Licences):
Party |
Position |
Name |
Telephone |
Contract 3901A Concrete Batching Facility (K. Wah Concrete Company Limited) |
Project Manager |
Benedict Wong |
9553 2806 |
Environmental Officer |
C P Fung |
9874 2872 |
|
Contract 3901B Concrete Batching Facility (Gammon Construction Limited) |
Senior Project Manager |
Gabriel Chan |
2435 3260 |
Environmental Officer |
Rex Wong |
2695 6319 |
The key activities of the
Project carried out in the reporting period included reclamation works and
land-based works. Works in the reclamation areas included marine filling,
seawall and facilities construction, together with runway and associated works
such as bored piling for approach lights. Land-based works on existing airport
island involved mainly airfield works, foundation and substructure work for
Terminal 2 expansion, modification and tunnel work for APM and BHS systems, and
preparation work for utilities, with activities include site establishment,
site office construction, road and drainage works, cable ducting, demolition of
existing facilities, piling, and excavation works.
The locations of key construction
activities are presented in Figure 1.1.
The status for all environmental
aspects are presented in Table
1.2. The EM&A requirements remained unchanged during the
reporting period.
Table 1.2: Summary of status for all environmental
aspects under the Updated EM&A
Manual
Parameters |
EM&A Requirements |
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 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 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 Baseline Water Quality 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. |
On-going for reclamation works. General impact water quality monitoring for water jetting works was completed on 23 May 2017. |
Initial Intensive Deep Cement Mixing (DCM) Water Quality Monitoring |
At least four weeks |
The Initial Intensive DCM Monitoring Report was submitted and approved by EPD in accordance with the Detailed Plan on DCM. |
Regular DCM Water Quality Monitoring |
Three times per week until completion of DCM works. |
Due to the completion of all marine-based DCM works within May 2021, regular DCM monitoring is ceased at all monitoring stations starting from 24 June 2021 and would be resumed if there are marine-based DCM works in the coming future. |
Sewerage and Sewage Treatment |
||
Methodology for carrying out annual sewage flow monitoring for concerned gravity sewer |
Methodology to be prepared and submitted to EPD one year before the scheduled commencement of operation of the proposed third runway |
The proposed methodology of the annual sewage flow monitoring was approved by EPD. The annual flow monitoring has been started since June 2021. |
Details of the routine H2S monitoring system for the sewerage system of 3RS |
Details to be prepared and submitted to EPD at least one year before commencement of the operation of 3RS |
The details of the routine H2S monitoring system will be prepared and submitted to EPD at least one year before commencement of operation of 3RS. |
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. |
The Supplementary CAP was submitted and approved by EPD under EP Condition 2.20. |
Contamination Assessment Report (CAR) for Golf Course |
CAR to be submitted for golf course |
The CAR for Golf Course was submitted and accepted by EPD. |
Contamination Assessment Reports (CAR) for Terminal 2 Emergency Power Supply Systems |
CAR to be submitted for Terminal 2 Emergency Power Supply Systems |
The CARs for Terminal 2 Emergency Power Supply Systems were submitted and accepted by EPD. |
Terrestrial Ecology |
||
Pre-construction Egretry Survey Plan |
Once per month in the breeding season between April and July, prior to the commencement of HDD drilling works. |
The 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. |
The terrestrial ecological monitoring at Sheung Sha Chau was completed in January 2019. |
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 |
- |
The coral translocation was completed. |
Post-Translocation Coral Monitoring |
As per an enhanced monitoring programme based on the Coral Translocation Plan |
The post-translocation monitoring programme according to the Coral Translocation Plan was completed in April 2018. |
Chinese White Dolphins (CWD) |
||
Baseline Monitoring |
6 months of baseline surveys before the commencement of land formation related construction works. Vessel line transect surveys: Two full surveys per month; Land-based theodolite tracking surveys: Two days per month at the Sha Chau station and two days per month at the Lung Kwu Chau station; and Passive Acoustic Monitoring (PAM): For the whole duration of baseline period. |
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 line transect surveys: Two full surveys per month; Land-based theodolite tracking surveys: 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. |
On-going |
Landscape & Visual |
|
|
Landscape & Visual Plan |
At least 3 months before the commencement of construction works on the formed land of the Project. |
The Landscape & Visual Plan was submitted and approved by EPD under EP Condition 2.18 |
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 and submitted to EPD under EP Condition 3.4. |
Impact Monitoring |
Weekly |
On-going |
Environmental Auditing |
|
|
Regular site inspection |
Weekly |
On-going |
Marine Mammal Watching Plan (MMWP) implementation measures |
Monitor and check |
On-going |
Dolphin Exclusion Zone (DEZ) Plan implementation measures |
Monitor and check |
On-going |
SkyPier High Speed Ferries (HSF) implementation measures |
Monitor and check |
On-going |
Construction and Associated Vessels Implementation measures |
Monitor and check |
On-going |
Silt Curtain Deployment Plan implementation measures |
Monitor and check |
On-going |
Spill Response Plan implementation measures |
Monitor and check |
On-going |
Complaint Hotline and Email channel |
Construction phase |
On-going |
Environmental Log Book |
Construction phase |
On-going |
Taking into account the construction works in
this reporting period, impact monitoring of air quality, noise, water quality,
waste management, landscape & visual, and CWD were carried out in the
reporting period.
The EM&A programme also involved weekly
site inspections and related auditing conducted by the ET for checking the
implementation of the required environmental mitigation measures recommended in
the approved EIA Report. To promote the environmental awareness and
enhance the environmental performance of the contractors, environmental
trainings and regular environmental management meetings were conducted
during the reporting period, which are summarised as below:
● Seventeen environmental management meetings for EM&A review with
works contracts: 2, 8, 9, 13, 14, 19, 21, 22, 23, 29 and 30 July 2021.
The EM&A programme has been following the
recommendations presented in the approved EIA Report and the 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 A.
Air quality monitoring of 1-hour Total
Suspended Particulates (TSP) was conducted three times every six days at two
representative monitoring stations in the vicinity of air sensitive receivers
in Tung Chung and villages in North Lantau in accordance with the Manual. Table 2.1
describes the details of the monitoring stations. Figure 2.1 shows the locations of the
monitoring stations.
Table 2.1:
Locations of Impact Air Quality Monitoring Stations
Monitoring Station |
Location |
AR1A |
Man Tung Road Park |
AR2 |
Village House at Tin Sum |
In accordance with the Manual, baseline air quality
monitoring of 1-hour TSP levels at the two air quality monitoring stations were
established as presented in the Baseline Monitoring Report. The Action and
Limit Levels of the air quality monitoring stipulated in the EM&A programme
for triggering the relevant investigation and follow-up procedures under the
programme are provided in Table
2.2.
Table 2.2: Action and Limit Levels of Air
Quality Monitoring
Monitoring Station |
Action Level (mg/m3) |
Limit Level (mg/m3) |
AR1A |
306 |
500 |
AR2 |
298 |
Portable direct reading dust meter was used to
carry out the air quality monitoring. Details of equipment used in the
reporting period are given in Table
2.3.
Table 2.3: Air Quality Monitoring
Equipment
Brand and Model |
Last Calibration Date |
Calibration Certificate Provided in |
|
Portable direct reading dust meter (Laser dust monitor) |
SIBATA LD-3B-2 (Serial No. 296098) |
20 Oct 2020 |
Monthly EM&A Report No. 58, Appendix E |
SIBATA LD-3B-1 (Serial No. 597337) |
10 May 2021 |
Monthly EM&A Report No. 65, Appendix D |
The
measurement procedures involved in the impact air quality monitoring can be
summarised as follows:
a.
The portable direct
reading dust meter was mounted on a tripod at a height of 1.2m above the
ground.
b.
Prior to the
measurement, the equipment was set up for 1 minute span check and 6 second
background check.
c.
The one hour dust
measurement was started. Site conditions and dust sources at the nearby area
were recorded on a record sheet.
d.
When the measurement
completed, the “Count” reading per hour was recorded for result calculation.
The portable direct reading dust
meter is calibrated every year against high volume sampler (HVS) to check the
validity and accuracy of the results measured by direct reading method. The
calibration record of the HVS provided in Appendix D of Construction Phase
Monthly EM&A Report No. 65, and the calibration certificates of portable direct reading dust meters listed in Table 2.3 are valid in the reporting period.
The air quality monitoring schedule involved in the reporting period is
provided in Appendix B.
The air
quality monitoring results in the reporting period are summarised in Table 2.4.
Detailed impact monitoring results are presented in Appendix C.
Table 2.4: Summary of Air Quality Monitoring Results
Monitoring Station |
1-hr TSP Concentration Range (mg/m3) |
Action Level (mg/m3) |
Limit Level (mg/m3) |
AR1A |
7 - 43 |
306 |
500 |
AR2 |
11 - 39 |
298 |
The monitoring results were within the
corresponding Action and Limit Levels at all monitoring stations in the
reporting period.
General meteorological conditions throughout
the impact monitoring period were recorded. Wind data including wind speed and
wind direction for each monitoring day were collected from the Chek Lap Kok Wind Station.
No dust emission source was observed at the
monitoring stations during the monitoring sessions. As the sensitive receivers
were far away from the construction activities, with the implementation of dust
control measures, there was no adverse impact at the sensitive receivers
attributable to the works of the Project.
Noise monitoring in the form of 30-minute
measurements of Leq, L10, and L90
levels was conducted once per week between 0700 and 1900 on normal weekdays at
four representative monitoring stations in the vicinity of noise sensitive
receivers in Tung Chung and villages in North Lantau in accordance with the
Manual. Table 3.1 describes the details of the monitoring stations. Figure 2.1 shows the locations of the
monitoring stations.
Table 3.1: Locations of Impact Noise
Monitoring Stations
Monitoring Station |
Location |
Type of measurement |
NM1A |
Man Tung Road Park |
Free field |
NM2(1) |
Tung Chung West Development |
To be determined |
NM3A(2) |
Site Office |
Facade |
NM4 |
Ching Chung Hau Po Woon Primary School |
Free field |
NM5 |
Village House in Tin Sum |
Free field |
NM6 |
House No. 1, Sha Lo Wan |
Free field |
Note:
(1) As described in Section 4.3.3 of the Manual, noise monitoring at NM2
will only commence after occupation of the future Tung Chung West Development.
(2) According to
Section 4.3.3 of the Manual, the noise monitoring at NM3A was temporarily
suspended starting from 1 September 2018 and would be resumed with the
completion of the Tung Chung East Development.
In accordance
with the Manual, baseline noise levels at the noise monitoring stations were
established as presented in the Baseline Monitoring Report. The Action and
Limit Levels of the noise monitoring stipulated in the EM&A programme for
triggering the relevant investigation and follow-up procedures under the
programme are provided in Table
3.2.
Table 3.2: Action and Limit Levels for Noise Monitoring
Monitoring Stations |
Time Period |
Action Level |
Limit Level, Leq(30mins) dB(A) |
NM1A, NM2, NM3A, NM4, NM5 and NM6 |
0700-1900 hours on normal weekdays |
When one documented complaint is received from any one of the sensitive receivers |
75dB(A)(1) |
Note:
(1) The Limit Level for NM4 is reduced to 70dB(A) for being an educational
institution. During school examination period, the Limit Level is further
reduced to 65dB(A).
Noise monitoring was performed using sound
level meter at each designated monitoring station. The sound level meters
deployed comply with the International Electrotechnical Commission Publications
651:1979 (Type 1) and 804:1985 (Type 1) specifications. Acoustic calibrator was
used to check the sound level meters by a known sound pressure level for field
measurement. Details of equipment used in the reporting period are given
in Table 3.3.
Table 3.3: Noise Monitoring
Equipment
Equipment |
Brand and Model |
Last Calibration Date |
Calibration Certificate Provided in |
Integrated Sound Level Meter |
Rion NL-52 (Serial No. 00998505) |
20 Mar 2021 |
Monthly EM&A Report No. 63, Appendix E |
Rion NL-52 (Serial No. 01287679) |
20 Jun 2021 |
Monthly EM&A Report No. 66, Appendix D |
|
Acoustic Calibrator |
Casella CEL-120/1 (Serial No. 2383737) |
20 Jun 2021 |
Monthly EM&A Report No. 66, Appendix D |
Castle GA607 (Serial No. 040162) |
20 Mar 2021 |
Monthly EM&A Report No. 63, Appendix E |
The
monitoring procedures involved in the noise monitoring can be summarised as
follows:
a. The sound level meter was set on a tripod at
least a height of 1.2m above the ground for free-field measurements at
monitoring stations NM1A, NM4, NM5 and NM6. A correction of +3dB(A) was applied
to the free field measurements.
b. Façade measurements were made at the monitoring
station NM3A.
c. Parameters such as frequency weighting, time
weighting and measurement time were set.
d. Prior to and after each noise measurement, the
meter was calibrated using the acoustic calibrator. If the difference in
the calibration level before and after measurement was more than 1dB(A), the
measurement would be considered invalid and repeat of noise measurement would
be required after re-calibration or repair of the equipment.
e. During the monitoring period, Leq, L10 and L90 were
recorded. In addition, site conditions and noise sources were recorded on
a record sheet.
f. Noise measurement results, when
higher than the baseline monitoring levels, were corrected with reference to
the baseline monitoring levels.
g. Observations were recorded when high intrusive
noise (e.g. dog barking, helicopter noise) was observed during the monitoring.
The
maintenance and calibration procedures are summarised below:
a. The microphone head of the sound level meter
was cleaned with soft cloth at regular intervals.
b. The meter and calibrator were sent to the
supplier or laboratory accredited under Hong Kong Laboratory Accreditation
Scheme (HOKLAS) to check and calibrate at yearly intervals.
Calibration certificates of the
sound level meters and acoustic calibrators used in the noise monitoring listed
in Table 3.3 are
valid in the reporting period.
The
noise monitoring schedule involved in the reporting period is provided in Appendix B.
The noise monitoring results in the reporting
period are summarised in Table
3.4.
Detailed impact monitoring results are presented in Appendix C.
Table 3.4: Summary of Construction Noise Monitoring Results
Monitoring Station |
Noise Level Range, dB(A) Leq (30mins) |
Limit Level, dB(A) Leq (30mins) |
NM1A(1) |
70 - 73 |
75 |
NM4(1)(3) |
60 - 63 |
70(2) |
NM5(1)(3) |
53 - 62 |
75 |
NM6(1)(3) |
60 - 70 |
75 |
Notes:
(1)
+3dB(A) Façade
correction included;
(2)
Reduced to 65dB(A)
during school examination periods at NM4. Pre-Secondary 1 Hong Kong Attainment
Test took place on 13 July during this reporting period.
(3)
Some of the noise
measurement results were higher than the baseline monitoring levels. In order
to reduce the influence of non-Project related noise on the monitoring results,
these measurement results were corrected with reference to the baseline
monitoring levels.
No complaints were received from any sensitive
receiver that triggered the Action Level. All monitoring results were also
within the corresponding Limit Levels at all monitoring stations in the
reporting period.
As the construction activities were far away
from the monitoring stations, major sources of noise dominating the monitoring
stations observed during the construction noise impact monitoring were traffic
noise near NM1A, school activities at NM4 and aircraft noise near NM6 during
this reporting period. It is considered that the monitoring work during the
reporting period was effective and there was no adverse impact attributable to
the Project activities.
Water quality monitoring of DO, pH,
temperature, salinity, turbidity and suspended solids (SS) was conducted three
days per week, at mid-ebb and mid-flood tides, at a total of 23 water quality
monitoring stations, comprising 12 impact (IM) stations, 8 sensitive receiver (SR)
stations and 3 control (C) stations in the vicinity of water quality sensitive
receivers around the airport island in accordance with the Manual. The purpose of water quality monitoring at the IM stations
is to promptly capture any potential water quality impact from the Project
before it could become apparent at sensitive receivers (represented by the SR
stations). Table 4.1
describes the details of the monitoring stations. Figure 4.1 shows the locations of the
monitoring stations.
Table 4.1: Monitoring Locations of Impact Water Quality Monitoring
Monitoring Station |
Description |
Coordinates |
|
|
|
Easting |
Northing |
C1 |
Control Station |
804247 |
815620 |
C2 |
Control Station |
806945 |
825682 |
C3(2) |
Control Station |
817803 |
822109 |
IM1 |
Impact Station |
807132 |
817949 |
IM2 |
Impact Station |
806166 |
818163 |
IM3 |
Impact Station |
805594 |
818784 |
IM4 |
Impact Station |
804607 |
819725 |
IM5 |
Impact Station |
804867 |
820735 |
IM6 |
Impact Station |
805828 |
821060 |
IM7 |
Impact Station |
806835 |
821349 |
IM8 |
Impact Station |
808140 |
821830 |
IM9 |
Impact Station |
808811 |
822094 |
IM10 |
Impact Station |
809794 |
822385 |
IM11 |
Impact Station |
811460 |
822057 |
IM12 |
Impact Station |
812046 |
821459 |
SR1A(1) |
Hong Kong-Zhuhai-Macao Bridge Hong Kong Boundary Crossing Facilities (HKBCF) Seawater Intake for cooling |
812660 |
819977 |
SR2 |
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 |
SR6A(3) |
Tai Ho Bay, Near Tai Ho Stream SSSI |
814739 |
817963 |
SR7 |
Ma Wan Fish Culture Zone (FCZ) |
823742 |
823636 |
SR8(4) |
Seawater Intake for cooling at Hong Kong International Airport (East) |
811623 |
820390 |
Notes:
(1)
With the operation of
HKBCF, water quality monitoring at SR1A station was commenced on 25 October
2018. To better reflect the water quality in the immediate vicinity of the
intake, the monitoring location of SR1A has been shifted closer to the intake
starting from 5 January 2019.
(2) 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.
(3) As the
access to SR6 was obstructed by the construction activities and temporary
structures for Tung Chung New Town Extension, the monitoring location has been
relocated to SR6A starting from 8 August 2019.
(4)
The monitoring location for SR8 is subject to further
changes due to silt curtain arrangements and the progressive relocation of this
seawater intake.
In accordance with the Manual, baseline water
quality levels at the above-mentioned representative water quality monitoring
stations were established as presented in the Baseline Water Quality Monitoring
Report. The
Action and Limit Levels of general water quality monitoring stipulated in the
EM&A programme for triggering the relevant investigation and follow-up
procedures under the programme are provided in Table 4.2. The control and impact
stations during ebb tide and flood tide for general water quality monitoring
are presented in Table 4.3.
Table 4.2: Action and Limit Levels for General Water Quality Monitoring
Parameters |
Action Level (AL) |
Limit Level (LL) |
||
Action and Limit Levels for general water quality monitoring (excluding SR1A & SR8) |
||||
DO in mg/l (Surface, Middle & Bottom) |
Surface and Middle 4.5mg/l |
Surface and Middle 4.1mg/l 5mg/l for Fish Culture Zone (SR7) only |
||
Bottom 3.4mg/l |
Bottom 2.7mg/l |
|||
Suspended Solids (SS) in mg/l |
23 |
or 120% of upstream control station at the same tide of the same day, whichever is higher |
37 |
or 130% of upstream control station at the same tide of the same day, whichever is higher |
Turbidity in NTU |
22.6 |
36.1 |
||
Action and Limit Levels SR1A |
|
|
|
|
SS (mg/l)) |
33 |
|
42 |
|
Action and Limit Levels SR8 |
|
|
|
|
SS (mg/l) |
52 |
|
60 |
|
Notes:
(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.
Table 4.3: The Control and Impact
Stations during Flood Tide and Ebb Tide for General Water Quality 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, SR6A, SR8 |
Ebb Tide |
|
C1 |
SR4A, SR5A, SR6A |
C2 |
IM1, IM2, IM3, IM4, IM5, IM6, IM7, IM8, IM9, IM10, IM11, IM12, SR1A, SR2, SR3, SR7, SR8 |
Note:
(1) As per findings of
Baseline Water Quality Monitoring Report, the control reference has been
changed from C3 to SR2 from 1 September 2016 onwards.
Table
4.4 summarises the
equipment used in the reporting period for monitoring of specific water quality
parameters under the water quality monitoring programme.
Table 4.4: Water Quality Monitoring Equipment
Brand and Model |
Last Calibration Date |
Calibration Certificate Provided in |
|
Multifunctional Meter (measurement of DO, pH, temperature, salinity and turbidity) |
YSI 6920V2 (Serial No. 0001C6A7) |
22 Apr 2021(1) |
Monthly EM&A Report No. 64, Appendix E |
YSI 6920V2 (Serial No. 0001CF6C) |
20 May 2021 |
Monthly EM&A Report No. 65, Appendix D |
|
YSI ProDSS (Serial No. 18A104824) |
18 Jun 2021 |
Monthly EM&A Report No. 66, Appendix D |
|
YSI ProDSS (Serial No. 15M100005) |
26 Jul 2021 |
||
YSI ProDSS (Serial No. 16H104234) |
22 Apr 2021(1) |
Monthly EM&A Report No. 64, Appendix E |
|
YSI ProDSS (Serial No. 16H104233) |
20 May 2021 |
Monthly EM&A Report No. 65, Appendix D |
|
YSI ProDSS (Serial No. 17E100747) |
18 Jun 2021 |
Monthly EM&A Report No. 66, Appendix D |
|
YSI ProDSS (Serial No. 17H105557) |
26 Jul 2021 |
||
Note:
(1) The monitoring
equipment was not used in the reporting period after the expiry date of the
calibration certificate.
Other equipment used as part of the impact
water quality monitoring programme are listed in Table 4.5.
Table 4.5: Other
Monitoring Equipment
Equipment |
Brand and Model |
Water Sampler |
Van Dorn Water Sampler |
Positioning Device (measurement of GPS) |
Garmin eTrex Vista HCx |
Current Meter (measurement of current speed and direction, and water depth) |
Sontek HydroSurveyor |
Water quality monitoring samples were
taken at three depths (at 1m below surface, at mid-depth, and at 1m above
bottom) for locations with water depth >6m. For locations with water depth
between 3m and 6m, water samples were taken at two depths (surface and bottom).
For locations with water depth <3m, only the mid-depth was taken. Duplicate water samples
were taken and analysed.
The water samples for all monitoring parameters
were collected, stored, preserved and analysed according to the Standard
Methods, APHA 22nd ed. and/or other methods as agreed by the EPD.
In-situ measurements at monitoring locations including temperature, pH, DO,
turbidity, salinity and water depth were collected by equipment listed in Table 4.4 and
Table 4.5.
Water samples for SS analysis were stored in high density polythene bottles
with no preservative added, packed in ice (cooled to 4ºC without being frozen),
delivered to the laboratory within 24 hours of collection.
Calibration
of In-situ Instruments
Wet bulb calibration for a DO meter was carried
out before commencement of monitoring and after completion of all measurements
each day. Calibration was not conducted at each monitoring location as daily
calibration is adequate for the type of DO meter employed. A zero check in
distilled water was performed with the turbidity probe at least once per
monitoring day. The probe was then calibrated with a solution of known NTU. In
addition, the turbidity probe was calibrated at least twice per month to establish
the relationship between turbidity readings (in NTU) and levels of SS (in
mg/l).
Calibration certificates of the monitoring
equipment used in the reporting period are listed in Table 4.4.
Analysis of SS have been carried out
by a HOKLAS accredited laboratory, ALS Technichem
(HK) Pty Ltd (Reg. No. HOKLAS 066). Sufficient water samples were collected at
all the monitoring stations for carrying out the laboratory SS determination.
The SS determination works were started within 24 hours after collection of the
water samples. The analysis of SS have followed the standard methods summarised
in Table 4.6. The
QA/QC procedures for laboratory measurement/ analysis of SS were presented in
Appendix F of the Construction Phase Monthly EM&A Report No.8.
Table
4.6: Laboratory
Measurement/ Analysis of SS
Parameters |
Instrumentation |
Analytical Method |
Reporting Limit |
SS |
Analytical Balance |
APHA 2540D |
2mg/l |
The water quality monitoring schedule for the
reporting period is updated and provided in Appendix B. Monitoring
sessions on 20 July 2021 was cancelled due to Strong Wind Signal No. 3 in
force.
The
water quality monitoring results for all parameters, except SS, obtained during
the reporting period were within their corresponding Action and Limit Levels. The detailed monitoring results
are presented in Appendix C.
For SS, some of the testing results triggered
the corresponding Action and Limit Levels, and investigations were conducted accordingly.
Table
4.7
to Table 4.8
present the summary of the SS compliance status at IM and SR stations during
mid-ebb and mid-flood tide for the reporting period.
Table 4.7: Summary of SS Compliance Status
(Mid-Ebb Tide)
Table 4.8: Summary of SS Compliance Status
(Mid-Flood Tide)
Note: Detailed results are presented in Appendix C. |
|
Legend: |
|
|
The monitoring results were within the corresponding Action and Limit Levels |
|
Monitoring result triggered the Action Level at monitoring station located upstream of the Project based on dominant tidal flow |
D |
Monitoring result triggered the Action Level at monitoring station located downstream of the Project based on dominant tidal flow |
|
Monitoring result triggered the Limit Level at monitoring station located upstream of the Project based on dominant tidal flow |
|
Upstream station with respect to the Project during the respective tide based on dominant tidal flow |
Monitoring results triggered the corresponding
Action and Limit Levels on two monitoring days. Some cases occurred at monitoring
stations upstream of the Project during flood tide and would unlikely be
affected by the Project.
In accordance with Event and Action Plan
stipulated in the Manual, EPD, IEC and Contractor were informed when the
corresponding Action or Limit Levels were triggered.
Investigation focusing on the case which
occurred at a monitoring station located downstream of the Project was carried
out. Details of the Project’s marine construction activities and site
observations of the concerned monitoring day were collected. Findings were
summarized in Table 4.9.
Table 4.9: Summary of Findings from
Investigation of SS Monitoring Results
Date |
Marine construction works nearby |
Approximate distance from marine construction works
|
Status of water quality measures (if applicable) |
Construction vessels in the vicinity |
Turbidity / Silt plume observed near the monitoring station |
Action or Limit Level triggered due to Project |
08/07/2021 |
Marine Piling |
At least 5.5km |
Silt curtain deployed |
No |
No |
No |
The investigation confirmed that marine piling
was conducted with silt curtains deployed during the concerned monitoring day.
The silt curtains were maintained properly and checked by ET regularly.
For SS result recorded in ebb tide at IM4 on 8
July 2021 which triggered the corresponding Action Level, no silt plume was
observed at this monitoring station and appropriate mitigation measures were
implemented properly by the contractor. No muddy water discharges from outfalls
of the reclaimed land were observed. Moreover, the location of IM4 was far away
(i.e. at least 5.5km) from the nearest marine construction activity of the
Project, so it was unlikely affected by the Project. Therefore, the case was
considered unlikely due to the Project.
During
the reporting period, it is noted that the vast majority of monitoring results
were within their corresponding Action and Limit Levels, while only a minor
number of SS measurement results triggered the corresponding Action and Limit
Levels, and investigations were conducted accordingly.
Based on the investigation findings, all
results that triggered the corresponding Action Level and Limit Levels were not
due to the Project. Therefore, the Project did not cause adverse impact at the
water quality sensitive receivers. All required actions under the Event and
Action Plan were followed. These cases appeared to be due to natural fluctuation
or other sources not related to the Project.
Nevertheless, as part of the EM&A
programme, the construction methods and mitigation measures for water quality
will continue to be monitored and opportunities for further enhancement will
continue to be explored and implemented where possible, to strive for better
protection of water quality and the marine environment.
In the meantime, the contractors were reminded
to implement and maintain all mitigation measures during weekly site inspection
and regular environmental management meetings. These include maintaining
mitigation measures properly for reclamation works including marine filling and
seawall construction as recommended in the Manual.
In accordance with the Manual, the waste
generated from construction activities was audited once per week to determine
if wastes are 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 5.1.
Table 5.1:
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 monitoring on all works contracts were
carried out by the ET to check and monitor the implementation of proper waste
management practices during the construction phase.
Recommendations made included provision and
maintenance of proper chemical waste storage area, as well as handling,
segregation, and regular disposal of general refuse. The contractors have taken
actions to implement the recommended measures. Waste management audits were
carried out by ET according to the requirement of the Waste Management Plan,
Updated EM&A Manual and the implementation schedule of the waste management
mitigation measures in Appendix A.
Based on updated information
provided by contractors, construction waste generated in the reporting period
is summarised in Table 5.2.
Proactive measures have been undertaken during the re-configuration of T2
building. The contractor has established the recycling strategy for
C&D materials with proper planning and design to maximize recycling and
reuse. Dedicated recyclers were employed for different kinds of
recyclable materials by the contractor, and ET and IEC have carried out site
visit to recyclers’ faciltities to review recycling
process. Dedicated areas for sorting of materials are established on
site. Recyclable materials such as steel, reinforcement bar, structural steel, aluminum, copper, other metals and glass are sorted on-site
and transported off-site for recycling. ET and IEC have carried out site audits
regularly and reviewed the trip ticket system.
Table 5.2: Construction Waste Statistics
|
C&D(1) Material Stockpiled for Reuse or Recycle (m3) |
C&D Material Reused in the Project (m3) |
C&D Material Reused in other Projects (m3) |
C&D Material Transferred to Public Fill (m3) |
Chemical Waste (kg) |
Chemical Waste (l) |
General Refuse (tonne) |
|
June 2021(2)(3) |
*17,809 |
*106,196 |
0 |
*5,169 |
120 |
*800 |
*1,235 |
|
July 2021(2)(4) |
28,937 |
106,079 |
381 |
4,514 |
0 |
0 |
1,582 |
|
Notes: (1) C&D refers to Construction and Demolition. (2) Metals, paper and/or plastics were recycled in the reporting period. (3) Updated figure for the previous month is reported and marked with an asterisk (*). Updated figures for earlier months will be reported in the forthcoming Quarterly and Annual EM&A Reports. (4) The data was based on the information provided by contractors up to the submission date of this Monthly EM&A Report, and might be updated in the forthcoming Monthly EM&A Report. |
There were no complaints, non-compliance of the
WMP, contract-specific WMPs, statutory and contractual requirements that
triggered Action and Limit Levels in the reporting period.
Along with the design and construction
progress, further development on the treatment level/details and the re-use
mode for marine sediment generated from 3RS Project has been conducted
according to the EIA recommendation.
Marine sediment is managed according to the EIA
Report, Updated EM&A Manual and Waste Management Plan of the Project. The
sampling process, storage conditions of the excavated marine sediment,
treatment process, final backfilling location as well as associated records
were inspected and checked by ET and verified by IEC to ensure they were in
compliance with the requirements as stipulated in the Waste Management Plan.
Sampling works for marine sediment generated
from the reclaimed land area was on-going during the reporting period. The
details of the marine sediment sampling, treatment and backfilling will be
reported in the subsequent EM&A Reports upon completion.
In accordance with the Manual, CWD monitoring by small vessel
line-transect survey supplemented by land-based theodolite tracking survey and
passive acoustic monitoring should be conducted during construction phase.
The small vessel line-transect survey should be
conducted at a frequency of two full surveys per month, while land-based
theodolite tracking survey should be conducted at a frequency of one day per
month per station at Sha Chau (SC) and Lung Kwu Chau
(LKC) during the construction phase as stipulated in the Manual.
The Action and Limit Levels for CWD monitoring
were formulated by the action response approach using the running quarterly
dolphin encounter rates STG and ANI derived from the baseline monitoring data,
as presented in the CWD Baseline Monitoring Report. The derived values of
Action and Limit Levels for CWD monitoring were summarised in Table 6.1.
Table
6.1: Derived
Values of Action and Limit Levels for Chinese White Dolphin Monitoring
|
NEL, NWL, AW, WL and SWL as a Whole |
Action Level(3) |
Running quarterly(1) STG < 1.86 & ANI < 9.35 |
Limit Level(3) |
Two consecutive running quarterly(2) (3-month) STG < 1.86 & ANI < 9.35 |
Notes: (referring to the baseline monitoring report) (1) Action Level – running quarterly encounter rates STG & ANI of this month will be calculated from the reporting period and the two preceding survey months. (2) Limit Level – two consecutive running quarters mean both the running quarterly encounter rates of the preceding month and the running quarterly encounter rates of this month. (3) Action Level and/or Limit Level will be triggered if both STG and ANI fall below the criteria. |
Small vessel line-transect surveys
were conducted along the transects covering Northeast Lantau (NEL), Northwest
Lantau (NWL), Airport West (AW), West Lantau (WL) and Southwest Lantau (SWL)
areas as proposed in the Manual, which are consistent with the Agriculture, Fisheries and Conservation
Department (AFCD) long-term monitoring programme (except the addition of AW).
The AW transect has not been previously surveyed in the AFCD programme due to
the restrictions of HKIA Approach Area, nevertheless, this transect was
established during the EIA of the 3RS Project and refined in the Manual with
the aim to collect project specific baseline information within the HKIA
Approach Area to fill the data gap that was not covered by the AFCD programme.
This also provided a larger sample size for estimating the density, abundance
and patterns of movements in the broader study area of the project.
The planned vessel survey transect lines
following the waypoints set for construction phase monitoring as proposed in
the Manual are depicted in Figure 6.1 with the waypoint coordinates
of all transect lines given in Table
6.2, which are subject to on-site refinement based on the
actual survey conditions and constraints.
Table 6.2: Coordinates of Transect Lines in NEL, NWL,
AW, WL and SWL Survey Areas
Waypoint |
Easting |
Northing |
Waypoint |
Easting |
Northing |
NEL |
|||||
1S |
813525 |
820900 |
6N |
818568 |
824433 |
1N |
813525 |
824657 |
7S |
819532 |
821420 |
2S |
814556 |
818449 |
7N |
819532 |
824209 |
2N |
814559 |
824768 |
8S |
820451 |
822125 |
3S |
815542 |
818807 |
8N |
820451 |
823671 |
3N |
815542 |
824882 |
9S |
821504 |
822371 |
4S |
816506 |
819480 |
9N |
821504 |
823761 |
4N |
816506 |
824859 |
10S |
822513 |
823268 |
5S |
817537 |
820220 |
10N |
822513 |
824321 |
5N |
817537 |
824613 |
11S |
823477 |
823402 |
6S |
818568 |
820735 |
11N |
823477 |
824613 |
NWL |
|||||
1S |
804671 |
814577 |
5S |
808504 |
821735 |
1N |
804671 |
831404 |
5N |
808504 |
828602 |
2Sb |
805475 |
815457 |
6S |
809490 |
822075 |
2Nb |
805476 |
818571 |
6N |
809490 |
825352 |
2Sa |
805476 |
820770 |
7S |
810499 |
822323 |
2Na |
805476 |
830562 |
7N |
810499 |
824613 |
3S |
806464 |
821033 |
8S |
811508 |
821839 |
3N |
806464 |
829598 |
8N |
811508 |
824254 |
4S |
807518 |
821395 |
9S |
812516 |
821356 |
4N |
807518 |
829230 |
9N |
812516 |
824254 |
AW |
|||||
1W |
804733 |
818205 |
2W |
805045 |
816912 |
1E |
806708 |
818017 |
2E |
805960 |
816633 |
WL |
|||||
1W |
800600 |
805450 |
7W |
800400 |
811450 |
1E |
801760 |
805450 |
7E |
802400 |
811450 |
2W |
800300 |
806450 |
8W |
800800 |
812450 |
2E |
801750 |
806450 |
8E |
802900 |
812450 |
3W |
799600 |
807450 |
9W |
801500 |
813550 |
3E |
801500 |
807450 |
9E |
803120 |
813550 |
4W |
799400 |
808450 |
10W |
801880 |
814500 |
4E |
801430 |
808450 |
10E |
803700 |
814500 |
5W |
799500 |
809450 |
11W |
802860 |
815500 |
5E |
801300 |
809450 |
12S/11E |
803750 |
815500 |
6W |
799800 |
810450 |
12N |
803750 |
818500 |
6E |
801400 |
810450 |
|
|
|
SWL |
|||||
1S |
802494 |
803961 |
6S |
807467 |
801137 |
1N |
802494 |
806174 |
6N |
807467 |
808458 |
2S |
803489 |
803280 |
7S |
808553 |
800329 |
2N |
803489 |
806720 |
7N |
808553 |
807377 |
3S |
804484 |
802509 |
8S |
809547 |
800338 |
3N |
804484 |
807048 |
8N |
809547 |
807396 |
4S |
805478 |
802105 |
9S |
810542 |
800423 |
4N |
805478 |
807556 |
9N |
810542 |
807462 |
5S |
806473 |
801250 |
10S |
811446 |
801335 |
5N |
806473 |
808458 |
10N |
811446 |
809436 |
Land-based theodolite tracking survey
stations were set up at two locations, one facing east/south/west on the
southern slopes of Sha Chau (SC), and the other facing
north/northeast/northwest at Lung Kwu Chau (LKC). The stations (D and E) are depicted in Figure 6.2 and shown in Table 6.3 with position coordinates,
height of station and approximate distance of consistent theodolite tracking
capabilities for CWD.
Table 6.3: Land-based Theodolite 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 |
Small vessel line-transect surveys provided data
for density and abundance estimation and other assessments using
distance-sampling methodologies, specifically, line-transect methods.
The surveys involved small vessel line-transect
data collection and have been designed to be similar to, and consistent with,
previous surveys for the AFCD for their long-term monitoring of small cetaceans
in Hong Kong. The survey was designed to provide systematic, quantitative
measurements of density, abundance and habitat use.
As mentioned in Section 6.2.1, the transects
covered NEL, NWL, AW, WL and SWL areas as proposed in the Manual, which are
consistent with the AFCD long-term monitoring programme (except AW). There are
two types of transect lines:
● Primary transect lines: the parallel
and zigzag transect lines as shown in Figure 6.1; and
● Secondary transect lines: transect
lines connecting between the primary transect lines and going around islands.
All data collected on both primary and
secondary transect lines were used for analysis of sighting distribution, group
size, activities including association with fishing boat, and mother-calf
pairs. Only on-effort data collected under favourable conditions of Beaufort
0-3 and visibility of approximately 1200 m or beyond were used for analysis of
the CWD encounter rates.
A 15-20m vessel with a flying bridge
observation platform about 4 to 5m above water level and unobstructed forward
view, and a team of three to four observers were deployed to undertake the
surveys. Two observers were on search effort at all times when following
the transect lines with a constant speed of 7 to 8 knots (i.e. 13 to 15 km per
hour), one using 7X handheld binoculars and the other using unaided eyes and recording
data.
During on-effort survey periods, the survey
team recorded effort data including time, position (waypoints), weather
conditions (Beaufort sea state and visibility) and distance travelled in each
series with assistance of a handheld GPS device. The GPS device also
continuously and automatically logged data including time, position (latitude
and longitude) and vessel speed throughout the entire survey.
When CWDs were seen, the survey team was taken
off-effort, the dolphins were approached and photographed for photo-ID
information (using a Canon 7D [or similar] camera and long 300 mm+ telephoto
lens), then followed until they were lost from view. At that point, the
boat returned (off effort) to the survey line at the closest point after obtaining
photo records of the dolphin group and began to survey on effort again.
Focal follows of dolphins would be used for
providing supplementary information only where practicable (i.e. when
individual dolphins or small stable groups of dolphins with at least one member
that could be readily identifiable with unaided eyes during observations and
weather conditions are favourable). These would involve the boat following (at
an appropriate distance to minimise disturbance) an identifiable individual
dolphin for an extended period of time, and collecting detailed data on its
location, behaviour, response to vessels, and associates.
CWDs can be identified by their
unique features like presence
of scratches, nick marks, cuts, wounds, deformities of their dorsal fin and
distinguished colouration and spotting patterns.
When CWDs were observed, the
survey team was taken off-effort, the dolphins were approached and photographed for photo-ID information
(using a Canon 7D [or similar] camera and long 300 mm+ telephoto lens). The
survey team attempted to photograph both sides of every single dolphin in the
group as the colouration and spotting pattern on both sides may not be
identical. The photos were taken at the highest available resolution and stored
on Compact Flash memory cards for transferring into a computer.
All photos taken were initially examined to
sort out those containing potentially identifiable individuals. These
sorted-out images would then be examined in detail and compared to the CWD
photo-identification catalogue established for 3RS Project during the baseline
monitoring stage.
Land-based theodolite tracking survey obtains fine-scale
information on the time of day and movement patterns of the CWDs. A
digital theodolite (Sokkia/Sokkisha Model DT5 or
similar equipment) with 30-power
magnification and 5-s precision was used to obtain the vertical and horizontal angle of each
dolphin and vessel position. Angles
were converted to geographic coordinates (latitude and longitude) and
data were recorded using Pythagoras software, Version 1.2. This
method delivers precise positions of multiple
spatially distant targets in a short period of time. The
technique is fully non-invasive, and allows for time and cost-effective
descriptions of dolphin habitat use patterns at all times of daylight.
Three surveyors (one theodolite operator, one
computer operator, and one observer) were involved in each survey. Observers
searched for dolphins using unaided eyes and handheld binoculars (7X50).
Theodolite tracking sessions were initiated whenever an individual CWD or group
of CWDs was located. Where possible, a distinguishable individual was
selected, based on colouration, within the group. The focal individual
was then continuously tracked via the theodolite, with a position recorded each
time the dolphin surfaced. In case an individual could not be positively
distinguished from other members, the group was tracked by recording positions
based on a central point within the group whenever the CWD surfaced. Tracking
continued until animals were lost from view; moved beyond the range of reliable
visibility (>1-3km, depending on station height); or environmental
conditions obstructed visibility (e.g., intense haze, Beaufort sea state >4,
or sunset), at which time the research effort was terminated. In addition
to the tracking of CWD, all vessels that moved within 2-3km of the station were
tracked, with effort made to obtain at least two positions for each vessel.
Theodolite tracking included focal follows of
CWD groups and vessels. Priority was given to tracking individual or groups of
CWD. The survey team also attempted to track all vessels moving within 1 km of
the focal CWD.
Within this reporting period, two
complete sets of small vessel line-transect surveys were conducted on the 12,
13, 14, 19, 21, 22, 26 and 28 July 2021, covering all transects in NEL, NWL,
AW, WL and SWL survey areas for twice.
A total of around 432.30 km of
survey effort was collected from these surveys and around 98.1% of the survey effort was being conducted
under favourable weather condition (i.e. Beaufort Sea
State 3 or below with favourable visibility). Details
of the survey effort are given in Appendix C.
Sighting Distribution
In July 2021, 30 sightings with
93 dolphins were sighted. Amongst these sightings, 29 sightings with 90
dolphins are on-effort records under favourable
weather condition (i.e. Beaufort Sea State 3 or below with favourable
visibility). Details of cetacean sightings are presented in Appendix C.
Distribution of all CWD sightings
recorded in July 2021 is illustrated in Figure 6.3. In WL, CWD
sightings were scattered between Tai O and Fan Lau with more CWD groups sighted
between Tai O and Yi O. In SWL, the majority of the CWD sightings were recorded
within or south to the Southwest Lantau Marine Park. After three months of nil
sighting in NWL between April and June 2021, CWD were re-occurring in NWL in
this reporting month. Three CWD sightings were sighted in Urmston
Road waters between Lung Kwu Tan and SCLKCMP while
other two CWD sightings were recorded at the southwestern corner of the survey
area. There was no CWD sighting recorded in NEL survey area during the
reporting period.
Figure 6.3: Sightings Distribution of
Chinese White Dolphins
Remarks: (1) Please note that there are 30 pink circles on
the map indicating the sighting locations of CWDs. Some of them were very close
to each other and therefore may appear overlapped on this distribution map. (2)
Marine park excludes land area and the landward boundary generally follows the
high water mark along the coastline.
Encounter Rate
Two types of dolphin encounter
rates were calculated based on the vessel survey data. They included the number
of dolphin sightings per 100 km survey effort (STG) and total number of
dolphins per 100 km survey effort (ANI) in the whole survey area (i.e. NEL,
NWL, AW, WL and SWL). In the calculation of dolphin encounter rates, only survey
data collected under favourable weather condition
(i.e. Beaufort Sea State 3 or below with favourable
visibility) were used. The formulae used for calculation of the encounter rates
are shown below:
Encounter Rate by Number of Dolphin
Sightings (STG)
Encounter Rate by Number of Dolphins
(ANI)
(Notes:
Only data collected under Beaufort 3 or below condition were used)
In July 2021, a total of around 424.23
km of survey effort were conducted under Beaufort Sea State 3 or below with favourable visibility, whilst a total number of 29
on-effort sightings with 90 dolphins were sighted under such condition.
Calculation of the encounter rates for the month are shown in Appendix C.
For the running quarter of the
reporting period (i.e., from May to July 2021), a total of around 1116.93 km of
survey effort were conducted under Beaufort Sea State 3 or below with favourable visibility, whilst a total number of 49
on-effort sightings and a total number of 145 dolphins from on-effort sightings
were obtained under such condition. Calculation of the running quarterly
encounter rates are shown in Appendix C.
The STG and ANI of CWD in the
whole survey area (i.e. NEL, NWL, AW, WL and SWL) during the month of July 2021
and during the running quarter are presented in Table 6.4 below and compared with the Action Level.
Although the running quarterly encounter rate ANI fall below the Action
Level, the Action Level is not triggered as the running quarterly STG remain
above the Action Level.
Table 6.4: Comparison of CWD Encounter
Rates of the Whole Survey Area with Action Levels
|
Encounter Rate (STG) |
Encounter Rate (ANI) |
July 2021 |
6.84 |
21.22 |
Running Quarter from May to July 2021(1) |
4.39 |
12.98 |
Action Level |
Running quarterly(1) STG < 1.86 & ANI < 9.35 |
|
Note: (1) Running quarterly encounter rates STG & ANI were calculated from data collected in the reporting period and the two preceding survey months, i.e. the data from May to July 2021, containing six sets of transect surveys for all monitoring areas. Action Level will be triggered if both STG and ANI fall below the criteria. |
Group Size
In July 2021, 30 groups of 93 dolphins
in total were sighted, and the average group size of CWDs was 3.10 dolphins per
group. Number of sightings with medium group size (i.e. 3-9 dolphins) was
slightly higher than that with small group size (i.e. 1-2 dolphins). There were
no CWD sightings with large group size (i.e. 10 or more dolphins).
Activities and Association with Fishing Boats
Eleven CWD sightings were
recorded engaging in feeding activities in July 2021 and four sightings were
observed in association with operating purse seiners. Two of these sightings
were recorded in WL and the other two were sighted in SWL.
Mother-calf
Pair
In July 2021, there were two CWD
sightings recorded with the presence of mother-and-unspotted juvenile pair.
These two sightings were recorded in NWL and WL respectively.
In
July 2021, a total number of 35 different CWD individuals were identified for totally
50 times. A summary of photo identification works is presented in Table 6.5.
Representative photos of these individuals are given in Appendix C.
Table 6.5: Summary of Photo Identification
Individual ID |
Date of Sighting (dd-mmm-yy) |
Sighting Group No. |
Area |
|
Individual ID |
Date of Sighting (dd-mmm-yy) |
Sighting Group No. |
Area |
NLMM001 |
22-Jul-21 |
4 |
WL |
|
WLMM001 |
12-Jul-21 |
4 |
SWL |
NLMM009 |
26-Jul-21 |
2 |
NWL |
|
|
22-Jul-21 |
3 |
WL |
NLMM013 |
26-Jul-21 |
1 |
NWL |
|
WLMM009 |
12-Jul-21 |
6 |
SWL |
|
|
2 |
NWL |
|
WLMM028 |
22-Jul-21 |
7 |
WL |
NLMM015 |
26-Jul-21 |
2 |
NWL |
|
|
|
9 |
WL |
NLMM023 |
28-Jul-21 |
3 |
NWL |
|
WLMM029 |
22-Jul-21 |
7 |
WL |
NLMM078 |
22-Jul-21 |
1 |
WL |
|
WLMM030 |
14-Jul-21 |
3 |
WL |
SLMM003 |
14-Jul-21 |
2 |
WL |
|
WLMM043 |
14-Jul-21 |
1 |
WL |
|
|
7 |
WL |
|
|
|
4 |
WL |
SLMM010 |
14-Jul-21 |
2 |
WL |
|
|
22-Jul-21 |
1 |
WL |
|
22-Jul-21 |
1 |
WL |
|
WLMM063 |
22-Jul-21 |
5 |
WL |
|
|
2 |
WL |
|
WLMM067 |
22-Jul-21 |
1 |
WL |
SLMM012 |
13-Jul-21 |
3 |
SWL |
|
WLMM073 |
12-Jul-21 |
5 |
SWL |
SLMM014 |
12-Jul-21 |
2 |
SWL |
|
WLMM076 |
14-Jul-21 |
6 |
WL |
|
14-Jul-21 |
5 |
WL |
|
|
22-Jul-21 |
1 |
WL |
SLMM023 |
13-Jul-21 |
3 |
SWL |
|
WLMM089 |
28-Jul-21 |
1 |
NWL |
SLMM027 |
13-Jul-21 |
3 |
SWL |
|
|
|
2 |
NWL |
SLMM034 |
13-Jul-21 |
3 |
SWL |
|
WLMM091 |
14-Jul-21 |
3 |
WL |
SLMM037 |
12-Jul-21 |
3 |
SWL |
|
WLMM092 |
14-Jul-21 |
3 |
WL |
|
13-Jul-21 |
2 |
SWL |
|
|
22-Jul-21 |
6 |
WL |
|
14-Jul-21 |
7 |
WL |
|
WLMM114 |
12-Jul-21 |
4 |
SWL |
SLMM045 |
22-Jul-21 |
2 |
WL |
|
|
13-Jul-21 |
3 |
SWL |
SLMM049 |
13-Jul-21 |
3 |
SWL |
|
WLMM122 |
22-Jul-21 |
1 |
WL |
SLMM060 |
13-Jul-21 |
1 |
SWL |
|
WLMM131 |
14-Jul-21 |
6 |
WL |
SLMM064 |
22-Jul-21 |
3 |
WL |
|
WLMM166 |
22-Jul-21 |
2 |
WL |
Survey Effort
Land-based
theodolite tracking surveys were conducted at LKC on 12 July 2021 and at
SC on 27 July 2021, with a total of two days of land-based theodolite tracking
survey effort accomplished in this reporting period. One CWD group was tracked
from LKC station during the reporting period. Information of survey effort and
CWD groups are presented in Table
6.6. Details of the survey effort are presented in Appendix C.
Table 6.6: Summary of Survey Effort and CWD
Group of Land-based Theodolite Tracking
Land-based Station |
No. of Survey Sessions |
Survey Effort (hh:mm) |
No. of CWD Groups Sighted |
CWD Group Sighting per Survey Hour |
Lung Kwu Chau |
1 |
6:00 |
1 |
0.17 |
Sha Chau |
1 |
6:00 |
0 |
0 |
TOTAL |
2 |
12:00 |
1 |
0.08 |
Underwater
acoustic monitoring using Passive Acoustic Monitoring (PAM) should be
undertaken during land formation related construction works. Both C-POD and
F-POD are considered as effective PAM devices in detecting CWD occurrence, and
F-POD was the main PAM device deployed where feasible. During this reporting
period, the F-POD was remained underwater and positioned at south of Sha Chau
Island inside the SCLKCMP (Figure
6.5). The F-POD was last deployed on 20 May 2021 and the next
re-deployment is scheduled in early August 2021 to retrieve the data for
analysis. Acoustic data would be reviewed to give an indication of CWDs
occurrence patterns and anthropogenic noise information. Analysis would involve
use of proprietary software for objective automated data analyses and
experienced analysts to perform visual validation for assessment of dolphin
detection. As the period of data collection and analysis takes about four
months, PAM results could not be reported in monthly intervals but report for
supplementing the annual CWD monitoring analysis.
During the reporting period, silt curtains were
in place by the contractor for marine filling, in which dolphin observers were
deployed by contractor in accordance with the MMWP. Overall, 2 to 7 dolphin
observation stations and teams of at least two dolphin observers were deployed
by the contractors for continuous monitoring of the DEZ for bored piling and
seawall construction works in accordance with the DEZ Plan. Trainings for the
proposed dolphin observers on the implementation of MMWP and DEZ monitoring
were provided by the ET prior to the aforementioned works, with a cumulative
total of 704 individuals being trained and the training records kept by the ET.
From the contractors’ MMWP observation records, no dolphin or other marine
mammals were observed within or around the silt curtains. As for DEZ monitoring
records, no dolphin or other marine mammals were observed within or around the
DEZs in this reporting month. These contractors’ records were also audited by
the ET during site inspection.
Audits of acoustic decoupling measures for
construction vessels were carried out during weekly site inspection and the
observations are summarised in Section 7.1. Audits of SkyPier high speed ferries route diversion and speed
control and construction vessel management are presented in Section 7.4
and Section 7.5 respectively.
Detailed analysis of CWD monitoring results
collected by small vessel line-transect survey will be provided in future
quarterly reports. Detailed analysis of CWD monitoring results collected by
land-based theodolite tracking survey and PAM will be provided in future annual
reports after a larger sample size of data has been collected.
Monitoring of CWD was conducted with
two complete sets of small vessel line-transect surveys and two days of
land-based theodolite tracking survey effort as scheduled. The running quarterly encounter
rates STG and ANI in the reporting period did not trigger the Action Level for
CWD monitoring.
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.
The weekly site inspection schedule of the construction works is provided in Appendix B. Bi-weekly site inspections
were also conducted by the IEC. Besides, ad-hoc site inspections were
conducted by ET and IEC if environmental problems were identified, or
subsequent to receipt of an environmental complaint, or as part of the
investigation work. These site inspections provided a direct means to reinforce
the specified environmental protection requirements and pollution control
measures in construction sites.
During site inspections, environmental
situation, status of implementation of pollution control and mitigation
measures were observed. Environmental documents and site records, including
waste disposal record, maintenance record of environmental equipment, and
relevant environmental permit and licences, were also checked on site. Observations
were recorded in the site inspection checklist and passed to the contractor
together with the recommended mitigation measures where necessary in order to advise contractors on
environmental improvement, awareness and on-site enhancement measures.
The observations were
made with reference to the following information during the site inspections:
· The EIA and EM&A requirements;
· Relevant environmental protection
laws, guidelines, and practice notes;
· The EP conditions and other
submissions under the EP;
· Monitoring results of EM&A
programme;
· Works progress and programme;
· Proposal of individual works;
· Contract specifications on
environmental protection; and
· Previous site inspection results.
Good site practices were observed in site
inspections during the reporting period. Advice were given when necessary to
ensure the construction workforce were familiar with relevant procedures, and
to maintain good environmental performance on site. Regular toolbox talks on
environmental issues were organised for the construction workforce by the
contractors to ensure understanding and proper implementation of environmental
protection and pollution control mitigation measures.
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 A.
Implementation of applicable landscape and
visual mitigation measures (reference to the environmental protection measures
CM1 – CM10 in Appendix A) was monitored in accordance
with the Manual. All measures undertaken by both the contractor and the
landscape contractor during the construction phase and first year of the
operation phase shall be audited by a landscape architect, as a member of the
ET, on a regular basis to ensure compliance with the intended aims of the
measures. Site inspections shall be undertaken at least once every two months
during the operation phase.
The implementation status of the
environmental protection measures are summarized below in Table 7.1. Examples of landscape and
visual mitigation measures are shown in Table 7.2. The monitoring programme for
detailed design, construction, establishment works and long term management (10
years) stages is presented in Table
7.3. Event and Action Plan for Landscape and Visual impacts
is stated in Table 7.4.
Table 7.1: Landscape and Visual –
Construction Phase Audit Summary
Landscape and Visual Mitigation Measures during Construction |
Implementation Status |
Relevant Contract(s) in the Reporting Period |
CM1- The construction area and contractor’s temporary works areas shall be minimised to avoid impacts on adjacent landscape. |
The implementation of mitigation measures were checked by ET during weekly site inspection and clarified by the Contractors during the monthly Environmental Management Meetings. Implementation of the measures CM5, CM6 and CM7 by Contractors was observed. |
3RS Project contracts |
CM2 – Reduction of construction period to practical minimum |
||
CM3 – Phasing of the construction stage to reduce visual impacts during the construction phase. |
||
CM4 – Construction traffic (land and sea) including construction plants, construction vessels and barges shall be kept to a practical minimum. |
||
CM5 – Erection of decorative mesh screens or construction hoardings around works areas in visually unobtrusive colours. |
||
CM6 – Avoidance of excessive height and bulk of site buildings and structures |
||
CM7 – Control of night-time lighting by hooding all lights and through minimisation of night working periods |
||
CM8 – All existing trees shall be carefully protected during construction. Detailed Tree Protection Specification shall be provided in the Contract Specification. Under this specification, the Contractor shall be required to submit, for approval, a detailed working method statement for the protection of trees prior to undertaking any works adjacent to all retained trees, including trees in contractor’s works areas |
Tree Protection Specifications have been provided in the relevant Contract Specifications respectively for implementation by the Contractors under the Project.
The Contractors’ performance on the implementation of the tree maintenance and protection measures were observed and checked by the ET weekly during construction period. |
3302, 3503, 3508, 3602, 3801
3802 (To be implemented) |
CM9 – Trees unavoidably affected by the works shall be transplanted where practical. A detailed Tree Transplanting Specification shall be provided in the Contract Specification, if applicable. Sufficient time for necessary tree root and crown preparation periods shall be allowed in the project programme |
Tree Transplanting Specifications have been provided in the relevant Contract Specifications respectively for implementation by the Contractors under the Project where trees will unavoidably be affected by the construction works.
The Contractors were required to submit Method Statements for tree transplanting prior to the transplanting works. Tree inspections were conducted by ET to check the tree transplanting works implemented by the Contractors on site.
The Contractors’ performance on the implementation of trees maintenance and protection measures on transplanted trees were observed and checked by the ET bi-monthly during the 12-month establishment period after the completion of each batch of transplanting works.
Long term management of the transplanted trees were currently monitored by ET annually. |
3503, 3508, 3801
3802 (To be implemented) |
CM 10 – Land formation works shall be followed with advanced hydroseeding around taxiways and runways as soon as practical |
To be implemented around taxiways and runways as soon as practicable. |
To be implemented |
Table 7.2: Examples of Landscape and
Visual Mitigation Measures in the Reporting Period
|
|
|
Erection of site hoardings around works area in unobtrusive colours (CM5) |
Avoidance of excessive height and bulk of site buildings (CM6) |
Control of night-time lighting by hooding and minimisation of night working period (CM7) |
|
|
|
General view of tree protection zone for retained tree (CM8) |
General view of a transplanted tree (CM9) |
|
In accordance with the EM&A
Manual, all existing trees shall be protected carefully during construction.
Trees unavoidably affected by the works shall be transplanted where practical.
In this reporting period, the cumulative total number of retained and
transplanted trees under the Project were 87 and 26, respectively. A total of 90 nos. trees (including 11 nos. retained
trees from Contract 3503 and 79 nos. provisional trees from Contract 3508) were
not located within their works areas and were excluded from the Project.
Moreover, seven trees under Contract 3508 were transplanted to their corresponding
receptor sites during this reporting period. Details of the retained
trees, transplanted trees and to-be-transplanted trees under the Project are
summarized in Table 7.5.
Photos of transplanted trees are presented in Table 7.7. Locations
of newly transplanted trees during the reporting period are presented in Figure 7.1.
Details of the retained trees are to
be discussed in the Quarterly EM&A reports.
Table 7.3: Monitoring Programme for Landscape and
Visual
Stage |
Monitoring Task |
Monitoring Report |
Form of Approval |
Frequency |
Detailed Design |
Checking of design works against the recommendations of the landscape and visual impact assessments within the EIA shall be undertaken during detailed design and tender stage, to ensure that they fulfil the intention of the mitigation measures. Any changes to the design, including design changes on site shall also be checked. |
Report by AAHK / PM confirming that the design conforms to requirements of EP. |
Approved by Client
|
At the end of the Detailed Design Phase |
Construction |
Checking of the contractor’s operations during the construction period. |
Report on Contractor's compliance, by ET |
Counter signature of report by IEC |
Weekly |
Establishment Works |
Checking of the planting works during the twelve-month Establishment Period after completion of each batch of transplanting works. |
Report on Contractor's compliance, by ET |
Counter signature of report by IEC |
Every two months |
Long Term Management (10 year) |
Monitoring of the long-term management of the planting works in the period up to 10 years after completion of each batch of transplanting works. |
Report on Compliance by ET or Maintenance Agency as appropriate |
Counter signature of report by Management Agency |
Annually |
Table 7.4: Event and Action Plan for Landscape and Visual
Event Action Level |
Action |
|||
|
ET |
IEC |
AAHK / PM |
Contractor |
Design Check |
Check final design conforms to the requirements of EP and prepare report. |
Check report. Recommend remedial design if necessary. |
Undertake remedial design if necessary. |
|
Non-conformity on one occasion |
Identify source. Inform IEC and AAHK / PM. Discuss remedial actions with IEC, AAHK / PM and Contractor. Monitor remedial actions until rectification has been completed. |
Check report. Check Contractor’s working method. Discuss with ET and Contractor on possible remedial measures. Advise AAHK / PM on effectiveness of proposed remedial measures. Check implementation of remedial measures. |
Notify Contractor. Ensure remedial measures are properly implemented. |
Amend working methods to prevent recurrence of non-conformity. Rectify damage and undertake additional action necessary. |
Repeated Non-conformity |
Identify source. Inform IEC and AAHK / PM. Increase monitoring frequency. Discuss remedial actions with IEC, AAHK / PM and Contractor. Monitor remedial actions until rectification has been completed. If non-conformity stops, cease additional monitoring. |
Check monitoring report. Check Contractor’s working method. Discuss with ET and Contractor on possible remedial measures. Advise AAHK / PM on effectiveness of proposed remedial measures. Supervise implementation of remedial measures. |
Notify Contractor. Ensure remedial measures area properly implemented. |
Amend working methods to prevent recurrence of non-conformity. Rectify damage and undertake additional action necessary. |
Table 7.5: Summary of the Number of Retained,
Transplanted and To-be-transplanted Trees in the Reporting Period
Existing |
|
|
|
|
Contract |
Retain (nos.) |
Transplanted (nos.) |
To-be-transplanted (nos.) |
|
Establishment Period |
Maintenance Period |
|||
3302 |
9 |
0 |
0 |
0 |
3503 |
8 |
6 |
3 |
0 |
3508(1) |
25 |
12 |
0 |
0 |
3602 |
2 |
0 |
0 |
0 |
3801 |
43 |
0 |
5(2) |
0 |
Sub-total |
87 |
18 |
8 |
0 |
Provisional |
|
|
|
|
Contract |
Retain (nos.) |
Transplanted (nos.) |
To-be-transplanted (nos.) |
|
3508(1) |
51 |
0 |
10 |
|
Sub-total |
51 |
0 |
10 |
|
Grand Total |
138 |
26 |
10 |
Notes:
(1) As some of the site areas have been handed
over to Contract 3508, Contractor of Contract 3508 is currently managing some
of the trees. Existing trees to be managed by Contract 3508 is subject to
change after initial tree surveys for each batch of site areas have been
conducted by the Contractor.
(2) Three
transplanted trees (CT1194, CT1794 and CT1795) were subsequently fell after
transplantation. Please refer to Table 7.6 for details.
Summary of the updated transplanted trees
and photos are presented in Table
7.6 and Table
7.7 respectively.
Table 7.6: Summary of the Transplanted Trees Updated in
the Reporting Period
Tree ID |
Transplant Date |
Management Stage |
Management Agency |
Remarks |
CT276 |
3 May 2018
|
Establishment period 4 May 2018 – May 2019 |
Contract 3801 |
Next inspection will be conducted in February 2022. Photos of the last inspection in February 2021 can be referred to Table 7.7 of the Construction Phase Monthly EM&A Report No.62. |
Long Term Management period Jun 2019 – May 2028 |
Southern Landside Petrol Filling Station |
|||
CT1253 |
4 May 2018
|
Establishment period 5 May 2018 – May 2019 |
Contract 3801 |
|
Long Term Management period Jun 2019 – May 2028 |
Southern Landside Petrol Filling Station |
|||
T835 |
22 Jan 2020 |
Establishment period 23 Jan 2020 – Jan 2021 |
Contract 3503
|
Next inspection will be conducted in February 2022. Photos of the last inspection in February 2021 can be referred to Table 7.7 of the Construction Phase Monthly EM&A Report No.62. |
Long Term Management period Feb 2021 – Jan 2030 |
||||
T836 |
13 Dec 2019 |
Establishment period 14 Dec 2020 – Jan 2021 |
Contract 3503
|
|
Long Term Management period Feb 2021 – Jan 2030 |
||||
T838 |
22 Jan 2020 |
Establishment period 23 Jan 2020 – Jan 2021 |
Contract 3503
|
|
Long Term Management period Feb 2021 – Jan 2030 |
||||
T812 |
21 Dec 2020 |
Establishment period 22 Dec 2020 – Dec 2021 |
Contract 3503 |
Next inspection will be conducted in August 2021. Photos of the last inspection in June 2021 can be referred to Table 7.7 of the Construction Phase Monthly EM&A Report No.66. |
T814 |
20 Dec 2020 |
Establishment period 21 Dec 2020 – Dec 2021 |
Contract 3503 |
|
T815 |
15 Dec 2020 |
Establishment period 16 Dec 2020 – Dec 2021 |
Contract 3503 |
|
T829 |
18 Dec 2020 |
Establishment period 19 Dec 2020 – Dec 2021 |
Contract 3503 |
|
T830 |
14 Dec 2020 |
Establishment period 15 Dec 2020 – Dec 2021 |
Contract 3503 |
|
T831 |
19 Dec 2020 |
Establishment period 20 Dec 2020 – Dec 2021 |
Contract 3503 |
|
T1493 |
6 July 2021
|
Establishment period 7 July 2021 – July 2022 |
Contract 3508 |
Next inspection will be conducted in August 2021. Photos of
the last inspection in July 2021 were shown in |
T1494 |
6 July 2021 |
Establishment period 7 July 2021 – July 2022 |
Contract 3508 |
|
T1495 |
10 July 2021 |
Establishment period 11 July 2021 – July 2022 |
Contract 3508 |
|
T1496 |
5 July 2021 |
Establishment period 6 July 2021 – July 2022 |
Contract 3508 |
|
T1497 |
5 July 2021 |
Establishment period 6 July 2021 – July 2022 |
Contract 3508 |
|
T1498 |
29 June 2021 |
Establishment period 30 June 2021 – July 2022 |
Contract 3508 |
|
T1499 |
29 June 2021 |
Establishment period 30 June 2021 – July 2022 |
Contract 3508 |
|
T1500 |
30 June 2021 |
Establishment period 1 July 2021 – July 2022 |
Contract 3508 |
|
T1501 |
30 June 2021 |
Establishment period 1 July 2021 – July 2022 |
Contract 3508 |
|
T1502 |
5 July 2021 |
Establishment period 6 July 2021 – July 2022 |
Contract 3508 |
|
T1503 |
6 July 2021 |
Establishment period 7 July 2021 – July 2022 |
Contract 3508 |
|
T1504 |
24 June 2021 |
Establishment period 25 June 2021 – July 2022 |
Contract 3508 |
|
CT1194 |
4 May 2018 |
Establishment period 5 May 2018 – May 2019 |
Contract 3801 |
NA |
Long Term Management period Jun 2019 – May 2028 |
Southern Landside Petrol Filling Station |
Uprooted and collapsed due to Typhoon Higos on 18 August 2020. Tree removal was conducted as recommended by tree specialist of the contractor of Southern Landside Petrol Filing Station. |
||
CT1794 |
3 May 2018 |
Establishment period 4 May 2018 – May 2019 |
Contract 3801 |
NA |
Long Term Management period Jun 2019 – May 2028 |
AsiaWorld-Expo |
The tree within the land parcel was acquired by the government for construction of emergency hospital to handle COVID19 pandemic at AsiaWorld-Expo. The tree was felled in late 2020. |
||
CT1795 |
3 May 2018 |
Establishment period 4 May 2018 – May 2019 |
Contract 3801 |
NA |
Long Term Management period Jun 2019 – May 2028 |
AsiaWorld-Expo |
The tree within the land parcel was acquired by the government for construction of emergency hospital to handle COVID19 pandemic at AsiaWorld-Expo. The tree was felled in late 2020. |
Table 7.7: Photos of the Existing
Transplanted Trees
Under 12-month Establishment Period: |
|||
|
|
|
|
T1498 |
T1499 |
T1500 |
|
|
|
|
|
T1501 |
T1504 |
|
|
Newly Transplanted Trees during the Reporting Period |
|||
|
|
|
|
T1493 |
T1494 |
T1495 |
|
Newly Transplanted Trees during the Reporting Period |
|||
|
|
|
|
T1496 |
T1497 |
T1502 |
|
|
|
||
T1503 |
|
||
The Supplementary CAP was submitted to EPD
pursuant to EP Condition 2.20. The CARs for Golf Course and T2 Emergency Power
Supply Systems (EPSS) were submitted to EPD in accordance with EP Condition 1.9
and the Supplementary CAP in which no land contamination issues were
identified. EPD has issued no further comment for aforesaid CARs. No
leakage was found after the removal of underground fuel pipelines of T2 EPSS
and all required additional photos have been submitted to EPD.
According to the approved supplementary CAP,
there are 3 remaining locations where site re-appraisal / additional site
investigation are proposed. Based on the latest construction information, there
is no development programme for these locations at this stage. As such, the
status of site re-appraisal/ additional site investigation shall be further
updated upon latest development programme is available.
The Marine Travel Routes and
Management Plan for High Speed Ferries of SkyPier
(the SkyPier Plan) was submitted to the Advisory
Council on the Environment for comment and subsequently submitted to and
approved by EPD in November 2015 under EP Condition 2.10. The approved SkyPier Plan is available on the dedicated website of the
Project. In the SkyPier Plan, AAHK has committed to
implement the mitigation measure of requiring HSFs of SkyPier
travelling between HKIA and Zhuhai / Macau to start diverting the route with
associated speed control across the area, i.e. Speed Control Zone (SCZ), with
high CWD abundance. The route diversion and speed restriction at the SCZ have
been implemented since 28 December 2015.
Due to the COVID-19 pandemic, all SkyPier HSF services to/from Zhuhai and Macau have been
suspended from 25 March 2020 until further notice. No ferry movement between
HKIA SkyPier and Zhuhai and Macau was recorded in
July 2021. Key audit findings for the SkyPier HSFs
travelling to/from Zhuhai and Macau against the requirements of the SkyPier Plan during the reporting period are summarised in Table 7.8.
The daily movement of all SkyPier
HSFs, including those not using the diverted route, in this reporting period
(i.e., 2 to 3 daily movements) were within the maximum daily cap of 125 daily
movements. Status of compliance with the annual daily average of 99 movements
will be further reviewed in the Annual EM&A Report.
As
updated by CLP Power, the construction works of the Hong Kong Offshore LNG
Terminal Project may affect the route diversion operation of the SkyPier HSFs from Q3 to Q4 2021. The captains were informed
on the issue and ET will continue to closely monitor the implementation of the SkyPier Plan in the period.
Table 7.8: Summary of Key Audit Findings
against the SkyPier Plan
Requirements in the SkyPier Plan |
1 to 31 July 2021 |
Total number of ferry movements recorded and audited for HSF to/from Zhuhai and Macau |
0 |
Use diverted route and enter / leave SCZ through Gate Access Points |
0 deviation |
Daily Cap for all SkyPier HSFs including those not using diverted route
|
2 to 3 daily movement (within the maximum daily cap - 125 daily movements) |
ET carried out the following actions during the
reporting period:
During the reporting period, ET was notified
that no dolphin sightings were recorded within the DEZ by the contractors. The ET checked the dolphin sighting record and relevant
records by the contractors to audit the implementation of DEZ.
The current status of submissions under the EP
up to the reporting period is presented in Table 7.9.
Table
7.9: Status of
Submissions under Environmental Permit
EP Condition |
Submission |
Status |
2.1 |
Complaint Management Plan |
Accepted / approved by EPD
|
2.4 |
Management Organizations |
|
2.5 |
Construction Works Schedule and Location Plans |
|
2.7 |
Marine Park Proposal |
|
2.8 |
Marine Ecology Conservation Plan |
|
2.9 |
Marine Travel Routes and Management Plan for Construction and Associated Vessels |
|
2.10 |
Marine Travel Routes and Management Plan for High Speed Ferries of SkyPier |
|
2.11 |
Marine Mammal Watching Plan |
|
2.12 |
Coral Translocation Plan |
|
2.13 |
Fisheries Management Plan |
|
2.14 |
Egretry Survey Plan |
|
2.15 |
Silt Curtain Deployment Plan |
|
2.16 |
Spill Response Plan |
|
2.17 |
Detailed Plan on Deep Cement Mixing |
|
2.18 |
Landscape & Visual Plan |
|
2.19 |
Waste Management Plan |
|
2.20 |
Supplementary Contamination Assessment Plan |
|
3.1 |
Updated EM&A Manual |
|
3.4 |
Baseline Monitoring Reports |
During the reporting period, environmental
related licenses and permits required for the construction activities were
checked. No non-compliance with environmental statutory requirements was
recorded. The environmental licenses and permits which are valid in the
reporting period are presented in Appendix E.
Complaints received in the previous
reporting period
As reported in the previous Monthly EM&A
Report, two complaints were received in the previous reporting period.
· A complaint regarding dust issue at
the eastern quay of the Project received on 21 June 2021; and
· A complaint regarding muddy water
from the Project received on 28 June 2021.
The cases were investigated by ET in accordance
with the Manual and the Complaint Management Plan of the Project. The findings
of investigation are presented below.
Complaint regarding dust issue received on 21
June 2021
With the information provided by the
complainant on 21 June 2021 and subsequently on 8 July 2021, ET recognised the
concerned areas and three identified related contractors and requested them to
provide information regarding the complaint. Based on the
information provided by the contractors, water trucks were assigned to carry
out regular water spraying along the concerned areas according to their dust
control management plan and provided their water spraying record for June and
July 2021. Based on the ET’s weekly site inspections and ad-hoc
inspection, no observation related to dust issue was recorded. A joint
inspection by EPD, ET, IEC and AAHK was arranged after receiving the complaint,
in which the contractor was reminded to provide and maintain adequate dust
mitigation measures for haul roads in site areas and review the effectiveness
of dust control measures regularly. ET also observed another contractor was
conducting water spraying at concerned area during ET’s site inspection.
Nevertheless, all contractors were reminded to continue implementing water
spraying properly and adequately at their work areas. ET and IEC would continue
to monitor contractors' dust suppression measures during environmental site
inspections and the implementation of these measures at the concerned area.
Hence, the complaint case was considered closed.
Complaint regarding muddy water received
on 28 June 2021
With the photo provided by the complainant, ET
recognised the concerned area and identified five related contractors and
requested them to provide information regarding the complaint. Based on
the information provided by the contractors, no illegal discharge along
the alleged area during 21 to 25 June 2021 was reported. The temporary drainage system from one of the related
contractors was operating properly for water storage, reuse and recycling
onsite; and the sedimentation tanks from another contractor was
installed on-site and confirmed their wastewater would be treated before
discharge. Based on the ET’s
weekly site inspections, no illegal discharge was identified in the checklists.
Both the temporary
drainage system and sedimentation
tanks were observed operating properly during the regular site
inspections in June. No wastewater discharge was observed at the alleged area
during IEC’s ad-hoc site inspection in late June. A joint inspection by
EPD, ET, IEC and AAHK was also arranged after receiving the complaint. For the licensed discharge point
near the alleged area, no discharge of muddy water was observed. No observation indicating any illegal
discharge of muddy water from the vessels and pipes in accordance with the
provided photo. Furthermore, the Hong Kong Observatory issued four Amber
Rainstorm Warning Signals on 22, 23 and 24 June which might suggest the heavy
rainfall might resulting in surface runoff at the alleged area. As such, ET
would remind the contractors to pay attention on the possibility of surface run
off, especially during rainy season and carry out further improvement on current measures if needed.
ET and IEC would continue to monitor 3RS water quality and conduct site
inspections to check contractors’ environmental practice and compliances.
Hence, the complaint case was considered closed.
Complaint received in this
reporting period
A complaint regarding dust issue at
3RS construction site
area was received on 13 July 2021. The
case is under investigation and findings of the investigation will be reported
in the next Monthly EM&A Report.
Neither notification of summons nor prosecution
was received during the reporting period.
Cumulative
statistics on complaints, notifications of summons and status of prosecutions
are summarised in Appendix F.
Key
activities anticipated in the next reporting period for the Project will
include the following:
Contract 3206 Main Reclamation Works
● Land-based ground improvement works;
● Seawall construction; and
● Marine filling.
Airfield Works:
Contract 3301 North Runway Crossover Taxiway
● Cable ducting works; and
● Paving works.
Contract 3302 Eastern Vehicular Tunnel Advance Works
● Cable laying and ducting
works;
● Backfilling and
reinstatement works; and
● Piling and structure
works;
Contract 3303 Third Runway and
Associated Works
● Footing and utilities
work;
● Piling work;
● Construction of approach
light;
● Operation of asphalt plant; and
● Cable laying and ducting
works.
Contract
3305 Airfield Ground Lighting System
● Genset installation; and
● Site establishment.
Contract 3307 Fire Training
Facility
● Architectural, Builder's
and Finishing works;
● Drainage and utilities
works; and
● Building
construction.
Third Runway Concourse:
Contract 3403 New Integrated Airport Centres Building
and Civil Works
● Architectural, Builder's
Work and Finishing works;
● Underground utilities
construction;
● Footing construction;
and
● Sheet piling and
grouting works.
Contract 3405 Third Runway Concourse Foundation and
Substructure Works
● Foundation works;
● Piling work;
● Excavation and
backfilling; and
● Road formation.
Terminal 2 Expansion:
Contract 3503 Terminal 2 Foundation
and Substructure Works
● T2 re-configuration;
● Excavation works;
● Utilities and road works; and
● Piling and structure works.
Contract 3508 Terminal 2 Expansion
Works
● Excavation and footing
construction;
● Site formation;
● Piling work; and
● Builders’ works.
Automated People Mover (APM) and Baggage Handling System (BHS):
Contract
3601 New Automated People Mover System (TRC Line)
● Pull out test for
guideway;
● Guidebeam installation; and
● Concreting work.
Contract 3602 Existing APM System Modification
Works
● Car modification;
● Formwork erection and;
● Concreting work.
Construction Support
(Facilities):
Contract 3721 Construction Support
Infrastructure Works
● Laying of drainage pipes
and ducts;
● Site clearance;
● Paving works; and
● Road works.
Contract 3722 Construction Support
Facilities
● Electrical and
mechanical installation; and
● Site establishment.
Contract 3723 Construction Support
Facilities
● Erection of site office;
● Electrical and mechanical
installation; and
● Sewage pump and treatment system
installation
Airport Support
Infrastructure:
Contract 3801 APM and BHS Tunnels
on Existing Airport Island
● Formwork and rebar
fixing;
● Backfilling;
● Hanger support
installation; and
● Demolition works.
Contract 3802 APM and BHS Tunnels
and Related Works
● Construction of Airside
Fire Station and marine sediment treatment plant;
● Installation of sheet
pipes and dewatering well;
● Pre-drilling;
● Ground investigation
works; and
● Ducting works.
Construction Support
(Services / Licenses):
Contract 3901A Concrete Batching
Facility
● Plant operation; and
● Material conveyor belt
construction.
Contract 3901B Concrete Batching
Facility
● Plant operation; and
● Foundation works for
conveyor belt.
The key environmental issues for the Project in
the coming reporting period expected to be associated with the construction
activities include:
● Generation of dust from construction
works and stockpiles;
● Noise from operating equipment and
machinery on-site;
● Generation of site surface runoffs
and wastewater from activities on-site;
● Water quality from marine filling;
● DEZ monitoring for seawall
construction and bored piling for approach lights;
● Implementation of MMWP for silt
curtain deployment;
● Sorting, recycling, storage and
disposal of general refuse and construction waste;
● Reuse of treated marine sediments
from piling and excavation works;
● Management of chemicals and
avoidance of oil spillage on-site; and
● Acoustic decoupling measures for
equipment on marine vessels.
The implementation of required mitigation
measures by the contractors will be monitored by the ET.
A tentative schedule of the planned
environmental monitoring work in the next reporting period is provided in Appendix B.
With reference to Appendix E of the 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.
The key activities of the Project
carried out in the reporting period included reclamation works and land-based
works. Works in the reclamation areas included marine filling, seawall and
facilities construction, together with runway and associated works such as
bored piling for approach lights. Land-based works on existing airport island
involved mainly airfield works, foundation and substructure work for Terminal 2
expansion, modification and tunnel work for APM and BHS systems, and
preparation work for utilities, with activities include site establishment,
site office construction, road and drainage works, cable ducting, demolition of
existing facilities, piling, and excavation works.
All the monitoring works
for construction dust, construction noise, water quality, construction waste,
landscape & visual, and CWD were conducted during the reporting period in
accordance with the Manual.
Monitoring results of construction dust, construction noise, construction waste, and CWD did not
trigger the corresponding Action and Limit Levels during the reporting
period.
The water quality monitoring results for all
parameters, except SS, obtained during the reporting period were within the
corresponding Action and Limit Levels stipulated in the EM&A programme.
Relevant investigation and follow-up actions will be conducted according to the
EM&A programme if the corresponding Action and Limit Levels are triggered.
For SS, some of the testing results triggered the relevant Action or Limit
Levels, and the corresponding investigations were conducted accordingly. The
investigation findings concluded that the cases were not related to the
Project. To conclude, the construction activities in the reporting period did
not introduce adverse impact to all water quality sensitive receivers.
Weekly site inspections of the construction
works were carried out by the ET to audit the implementation of proper
environmental pollution control and mitigation measures for the Project.
Bi-weekly site inspections were also conducted by the IEC. Site inspection
findings were recorded in the site inspection checklists and provided to the
contractors to follow up.
On the implementation of the SkyPier Plan, due to the COVID-19 pandemic, all SkyPier HSF services to/from Zhuhai and Macau have been
suspended from 25 March 2020 until further notice. No HSF movement between HKIA SkyPier and
Zhuhai and Macau was recorded during the reporting period. Therefore, no
deviation was recorded in the HSF monitoring in the reporting period. The daily
movements of all SkyPier HSFs in the reporting
period, including those not using the diverted route, were in the range of 2 to
3 daily movements, which are within the maximum daily cap of 125 daily
movements.
On the implementation of MTRMP-CAV, the MSS
automatically recorded the deviation case such as speeding, entering no entry
zone and not travelling through the designated gates. ET conducted checking to
ensure the MSS records all deviation cases accurately. A training has been
provided for the concerned skipper to facilitate them in familiarising with the
requirements of the MTRMP-CAV. Deviations including speeding in the works area,
entered no entry zone, and entry from non-designated gates were reviewed by ET.
All the concerned captains were reminded by the contractor’s CTCC
representative to comply with the requirements of the MTRMP-CAV. The ET
reminded contractors that all vessels shall avoid entering the no-entry zone,
in particular the Brothers Marine Park and the Sha Chau & Lung Kwu Chau Marine Park. Three-month rolling programmes for
construction vessel activities, which ensures the proposed vessels are
necessary and minimal through good planning, were also received from
contractors.
[1] The Manual is available on the
Project’s dedicated website (accessible at: http://env.threerunwaysystem.com/en/index.html).