Contract
No: HK/2015/01 Wanchai Development Phase II and Central Wanchai
Bypass Sampling, Field Measurement and
Testing Work (Stage 3) Environmental
Permit no. EP-356/2009, Further
Evironmental permit nos. fep-02/356/2009, FEP-03/356/2009, Fep-04/356/2009 Fep-06/356/2009 and FEP-07/356/2009 Quarterly Environmental Monitoring
and Audit Report
- June 2016 to August 2016 -
|
CLIENTS: |
|
Civil
Engineering and Development Department and Highways
Department |
Lam Geotechnics
Limited 11/F Centre
Point 181-185 Gloucester Road, Wanchai, H.K. Telephone: (852) 2882-3939 Facsimile: (852) 2882-3331 E-mail: info@lamenviro.com Website: http://www.lamenviro.com |
|
|
|
|
|
CHECKED by: |
|
Raymond Dai Environmental Team Leader |
|
DATE: |
|
29 September
2016 |
2.2 Scope of the Project and Site Description
2.3 Division
of the Project Responsibility
2.4 Project
Organization and Contact Personnel
2.5 Principal Work and Activities
5.5. Review of the Reasons for and the Implications of
Non-compliance
5.6. Summary of action taken in the event of and follow-up
on non-compliance
6. Complaints, Notification of Summons
and Prosecution
7. Cumulative
Construction Impact due to the Concurrent Projects
lIST
OF TABLES
Table I Principal Work
Activities for Contract no. HK/2009/01
Table II Principal Work
Activities for Contract no. HK/2009/02
Table III Principal Work Activities
for Contract no. HY/2009/15
Table IV Principal Work
Activities for Contract no. HY/2009/19
Table V Principal Work
Activities for Contract no. HK/2012/08
Table VI Principal Work Activities for Contract no. HY/2010/08
Table 2.1 Schedule 2 Designated
Projects under this Project
Table 2.2 Details of Individual
Contracts under the Project
Table 2.3 Contact Details of
Key Personnel
Table 2.4 Principal Work Activities for Contract no. HK/2009/01
Table 2.5 Principal Work Activities for Contract no. HK/2009/02
Table 2.6 Principal Work
Activities for Contract no. HY/2009/15
Table 2.7 Principal Work
Activities for Contract no. HY/2009/19
Table 2.8 Principal Work Activities for Contract no. HK/2012/08
Table 2.9 Principal Work Activities for Contract no. HY/2010/08
Table 3.1 Noise Monitoring Stations
Table 3.2 Air Monitoring
Stations
Table 3.3 Marine Water Quality
Stations for Water Quality Monitoring
Table 3.4 Marine Water Quality
Monitoring Frequency and Parameters
Table
3.5 Marine Water Quality Stations for Enhanced Water
Quality Monitoring
Table 4.1 Noise Monitoring Station for Contract nos. HK/2009/01
and HK/2009/02
Table 4.2 Noise Monitoring
Station for Contract nos. HY/2009/15
Table 4.3 Noise Monitoring Stations for Contract no. HY/2009/19
Table 4.4 Noise Monitoring Stations for Contract no. HY/2010/08
Table 4.5 Air Monitoring Stations for Contract no. HK/2009/01
Table 4.6 Air Monitoring Station for Contract no. HK/2009/02
Table 4.7 Air Monitoring Station
for Contract no. HY/2009/15
Table 4.8 Air Monitoring Stations for Contract no. HY/2009/19
Table 4.9 Air Monitoring Station
for Contract no. HK/2012/08
Table 4.10 Air Monitoring Stations for Contract no. HY/2010/08
Table 4.11 Water Monitoring Stations for Contract no. HK/2009/01
Table 4.12 Water Monitoring Stations for
Contract no. HK/2009/02
Table 4.13 Water Monitoring Stations for Contract no. HK/2012/08
Table 4.14 Water Monitoring Stations
for Contract no. HY/2009/15
Table 4.15 Enhance Dissolved Oxygen
Monitoring Stations for Contract no. HY/2009/15
Table 4.16 Water quality monitoring Stations for Contract no. HY/2010/08
Table 4.17 Enhance Dissolved
Oxygen Monitoring Stations for Contract no. HY/2010/08
Table 4.18 Details of Waste
Disposal for Contract no. HK/2009/01
Table 4.19 Details of Waste
Disposal for Contract no. HK/2009/02
Table 4.20 Details
of Waste Disposal for Contract no. HY/2009/15
Table 4.21 Details of Waste Disposal for Contract no. HY/2009/19
Table 4.22 Details of
Waste Disposal for Contract no. HK/2012/08
Table 4.23 Details of Waste Disposal for
Contract no. HY/2010/08
Table 6.1 Cumulative Statistics
on Complaints
Table 6.2 Cumulative Statistics
on Successful Prosecutions
lIST OF FIGUREs
Figure
2.1 Project Layout
Figure
2.2 Project Organization Chart
Figure 3.1 Locations of Environmental Monitoring
Stations
lIST OF APPENDIces
Appendix
2.1 Environmental Mitigation
Implementation Schedule
Appendix 3.1 Action and Limit Level
Appendix
4.1 Noise Monitoring
Graphical Presentations
Appendix
4.2 Air Quality Monitoring
Graphical Presentations
Appendix
4.3 Water Quality Monitoring
Graphical Presentations
Appendix 5.1 Event Action Plans
Appendix 6.1 Complaint Log
Appendix 7.1 Construction Programme of
Individual Contracts
Construction Activities for the
Reported Period
Table I Principal Work Activities for Contract
no. HK/2009/01
June 2016 |
July 2016 |
August 2016 |
Nil |
Nil |
Nil |
Table II Principal Work Activities for Contract no.
HK/2009/02
June 2016 |
July 2016 |
August 2016 |
Nil |
Nil |
Nil |
Table III
Principal Work Activities for
Contract no. HY/2009/15
June 2016 |
July 2016 |
August 2016 |
·
Reinstatement of vertical seawall at TPCWAE ·
Removal of temporary reclamation at TPCWAW |
·
Reinstatement of vertical seawall at TPCWAE ·
Removal of temporary reclamation at TPCWAW ·
Diaphragm wall cutting works at TPCWAW |
·
Reinstatement of vertical seawall at TPCWAE ·
Removal of temporary reclamation at TPCWAW ·
Diaphragm wall cutting works at TPCWAW |
Table IV Principal Work Activities for Contract no. HY/2009/19
June 2016 |
July 2016 |
August 2016 |
Nil |
Nil |
Nil |
Table V Principal Work Activities for Contract no.
HK/2012/08
June 2016 |
July 2016 |
August 2016 |
Precast unit construction for Box 1
inside Dry dock Construction of culvert L Bay 8, Bay
12 and Bay 13 |
Precast unit construction for Box 1
inside Dry dock Construction of culvert L Bay 8, Bay
12 and Bay 13 |
Precast unit construction for Box 1
inside Dry dock Construction of culvert L Bay 8, Bay 12 and Bay
13 |
Table VI
Principal Work Activities for Contract
no. HY/2010/08
June 2016 |
July 2016 |
August 2016 |
Diversion pipe maintenance Diaphragm Wall Removal Works |
Diversion pipe maintenance Diaphragm Wall Removal Works |
Diversion pipe maintenance Diaphragm Wall Removal Works |
Noise Monitoring
Air Quality Monitoring
CMA6a monitoring station was rescheduled
from 7 June 2016 to 8 June 2016.
CMA1b monitoring station was rescheduled
from 5 July 2016 to 6 July 2016.
CMA2a monitoring station was rescheduled
from 16 July 2016 to 18 July 2016.
CMA5b monitoring station was rescheduled
from 11 July 2016 to 12 July 2016.
Water Quality Monitoring
Complaints, Notifications of
Summons and Successful Prosecutions
1.1.1.
Lam
Geotechnics Limited (LGL) has been appointed to work as the Environmental Team
(ET) under Environmental Permit no. EP-356/2009 and Further Environmental
permit nos. FEP-02/356/2009,
FEP-03/356/2009,
FEP-04/356/2009, FEP-06/356/2009 and FEP-07/356/2009 to
implement the Environmental Monitoring and Audit (EM&A) programme as
stipulated in the EM&A Manual of the approved Environmental Impact
Assessment (EIA) Report for Wan Chai Development phase II and Central-Wan Chai
Bypass (Register No.: AEIAR-125/2008) and in the EM&A Manual of the approved
EIA Report for Central-Wan Chai Bypass and Island Eastern Corridor Link
(Register No. AEIAR-041/2001).
1.1.2.
This
report presents the environmental monitoring and auditing work carried out in
accordance to the Section 10.4 of EM&A Manual and “Environmental
Monitoring and Audit Requirements” under Particular
Specification Section 27.
1.1.3.
This report documents the finding of EM&A works
during the period from 27th May 2016 to 26th
August 2016.
Section 1 Introduction – details the scope and structure of the
report.
Section 2 Project Background – summarizes background and scope of the
project, site description, project organization and contact details of key
personnel during the reporting period.
Section 3 Monitoring Requirements – summarizes all monitoring parameters,
monitoring locations, monitoring frequency, duration and action plan.
Section 4 Monitoring Results – summarizes the monitoring results
obtained in the reporting period.
Section 5 Compliance Audit – summarizes the auditing of monitoring results, all
exceedances environmental parameters.
Section 6 Complaints,
Notification of summons and Prosecution – summarizes the cumulative
statistics on complaints, notification of summons and prosecution
Section 7 Cumulative
Construction Impact due to the Concurrent Projects – summarizes the
relevant cumulative construction impact due to the concurrent activities of the
concurrent Projects.
Section 8 Conclusion
2.1.1.
“Wan
Chai Development phase II and Central-Wan Chai Bypass” and “Central-Wan Chai
Bypass and Island Eastern Corridor Link” (hereafter called “the Project”) are
Designed Project (DP) under the Environmental Impact Assessment Ordinance (Cap.
499) (EIAO). The Environmental Impact
Assessment (EIA) Reports for Central-Wan Chai Bypass and Island Eastern
Corridor Link (Register No. AEIAR-041/2001) and Wan Chai Development phase II
and Central-Wan Chai Bypass (Register No.: AEIAR-125/2008) have been approved
on 31 August 2001 and 11 December 2008 respectively.
2.1.2.
The
key purpose of Wan Chai Development Phase II (WDII) is to provide land at Wan
Chai North and North Point for construction of the Central-Wan Chai Bypass and
Island Eastern Corridor Link (CWB). Land formed under the project will be
developed as a world-class waterfront promenade joining that at the new Central
waterfront for public enjoyment.
2.1.3.
There
is a compelling and present need for the CWB to provide relief to the very
congested east-west Connaught Road Central/Harcourt Road / Gloucester Road Corridor
(the Corridor) which is currently operating beyond its capacity. The CWB will
provide relief to the existing congestion along the Corridor and cater for the
anticipated growth of traffic on Hong Kong Island. Without the CWB and its
access roads, there will not be sufficient capacity to serve the heavy traffic
demands at both strategic and local levels.
2.2.1.
The
Project is located mainly in Wan Chai North, Causeway Bay and North Point, and
is demarcated by Gloucester Road and Victoria Park Road to the south, Fenwick
Pier Street to the west and Tong Shui Road Interchange to the east, as shown in
Figure 2.1.
2.2.2.
The
study area encompasses existing developments along the Wan Chai, Causeway Bay
and North Point shorelines. Major land uses include the Hong Kong Convention
& Exhibition Centre (HKCEC) Extension, the Wan Chai Ferry Pier, the ex-Wan
Chai Public Cargo Working Area (ex-PCWA), the Royal Hong Kong Yacht Club
(RHKYC), the Police Officers' Club, the Causeway Bay Typhoon Shelter (CBTS) and
commercial and residential developments.
2.2.3.
The scope of the Project comprises:
·
Land formation for key transport infrastructure and
facilities, including the Trunk Road (i.e. CWB) and the associated slip roads for
connection to the Trunk Road and for through traffic from Central to Wan Chai and
Causeway Bay. The land formed for the above transport infrastructure will provide
opportunities for the development of an attractive waterfront promenade for the
enjoyment of the public
·
Reprovisioning / protection of the existing
facilities and structures affected by the land formation works mentioned above
·
Extension, modification, reprovisioning or
protection of existing storm water drainage outfalls, sewerage outfalls and
watermains affected by the revised land use and land formation works mentioned
above
·
Upgrading of hinterland storm water drainage system
and sewerage system, which would be rendered insufficient by the land formation
works mentioned above
·
Provision of the ground level roads, flyovers,
footbridges, necessary transport facilities and the associated utility services
·
Construction of the new waterfront promenade,
landscape works and the associated utility services
·
The Trunk Road (i.e. CWB) within the study area and
the associated slip roads for connection to the Trunk Road.
2.2.4.
The
project also contains various Schedule 2 DPs that, under the EIAO, require
Environmental Permits (EPs) to be granted by the DEP before they may be either
constructed or operated. Table 2.1 summarises the five
individual DPs under this Project. Figure 2.1 shows the locations of these Schedule 2 DPs.
Table
2.1 Schedule 2 Designated Projects
under this Project
Item |
Designated Project |
EIAO Reference |
Reason for inclusion |
DP1 |
Central-Wanchai Bypass (CWB) including its road tunnel and slip roads |
Schedule 2, Part I, A.1 and A.7 |
Trunk road and road tunnel more than 800 m in length |
DP2 |
Road P2 and other roads which are classified as primary/district
distributor roads |
Schedule 2, Part I, A.1 |
Primary / district distributor roads |
DP3 |
Reclamation works including associated dredging works |
Schedule 2, Part I, C.1 and C.12 |
Reclamation more than 5 ha in size and a dredging operation less than
100 m from a seawater intake point |
DP5 |
Wan Chai East Sewage Outfall |
Schedule 2, Part I, F.5 and F.6 |
Submarine sewage pipelines with a total diameter more than 1,200 mm
and include a submarine sewage outfall |
DP6 |
Dredging for the Cross-harbour Water Mains from Wan Chai to Tsim Sha
Tsui |
Schedule 2, Part I, C.12 |
A dredging operation less than 100 m from a seawater intake point |
2.3.1
Due to the multi-contract nature of the Project, the status of permits
and/or licences under the individual contract(s) are presented as below:
Contract no. HK/2010/06 – Wan Chai
Development Phase II – Central – Wan Chai Bypass over MTR Tsuen Wan Line under
FEP-05/356/2009
2.3.2
The construction works were completed and the FEP-05/356/2009 was
surrendered by the Contractor on 3 October 2014.
Contract no. HY/2009/11 – Wan Chai
Development Phase II – Central – Wan Chai Bypass - North Point Reclamation
2.3.3
The construction works were completed and the FEP-01/356/2009 was
surrendered by the Contractor on 22 October 2012.
2.3.4
Due to the multi-contract nature of the Project, there are a
number of contracts sub-dividing the whole works area into different work areas
to be commenced. Contractors of
individual contracts will be required by the EP holder to apply Further
Environmental Permits (FEP) such that the impact monitoring stations are
sub-divided accordingly to facilitate the implementation of EM&A programme
and to streamline the EM&A reporting for individual FEP holders
correspondingly.
2.3.5
The details of individual contracts are summarized in Table2.2.
Table
2.2 Details of Individual Contracts
under the Project
Contract
No. |
Contract Title |
Associated
DP(s) |
Construction
Commencement Date |
HK/2009/01 |
Wan Chai Development Phase II – Central –Wanchai Bypass at Hong Kong
Convention and Exhibition Centre |
DP3, DP6 |
23 July 2010 |
DP1, DP2 |
25 August 2011 |
||
HK/2009/02 |
Wan Chai Development Phase II – Central – Wan Chai Bypass at WanChai
East |
DP3, DP5 |
5 July 2010 |
DP1 |
26 April 2011 |
||
HY/2009/11 |
Wan Chai Development Phase II and Central – Wan Chai Bypass – North
Point Reclamation |
DP3 |
17 March 2010 (Completed) |
HY/2009/15 |
Central-Wanchai Bypass – Tunnel (Causeway Bay Typhoon Shelter Section) |
DP3 |
10 November 2010 |
DP1 |
13 July 2011 |
||
HK/2010/06 |
Wan Chai Development Phase II-Central-Wan Chai Bypass over MTR Tsuen
Wan Line |
DP3 |
22 March 2011 (Completed) |
04/HY/2006 |
Reconstruction of Bus Terminus near Man Yiu Street and Man Kwong
Street |
DP1 |
September 2010 (Completed) |
HY/2009/17 |
Central - Wan Chai Bypass (CWB) at FEHD Whitfield Depot - Advanced
piling works. |
DP1 |
5 October 2010 (Completed) |
HY/2009/18 |
Central - Wan Chai Bypass (CWB) – Central Interchange |
DP1 |
10 March 2014 |
HY/2009/19 |
Central - Wanchai Bypass Tunnel (North Point Section) and Island
Eastern Corridor Link |
DP1 |
24 March 2011 |
HK/2012/08 |
Wan Chai
Development Phase II Central- Wan Chai Bypass at
Wan Chai West |
DP1,DP2,
DP3 |
5 March 2013 |
HY/2011/08 |
Central-Wan Chai
Bypass (CWB) – Tunnel Buildings, Systems and Fittings, and Works Associated
with Tunnel Commissioning |
DP1 |
8 October 2014 |
2.4.1.
Civil Engineering and Development Department and
Highways Department are the overall project controllers for the Wan Chai
Development Phase II and Central-Wan Chai Bypass respectively.
For the construction phase of the Project, Project Engineer, Contractor(s),
Environmental Team and Independent Environmental Checker are appointed to
manage and control environmental issues.
2.4.2.
The
proposed project organization and lines of communication with respect to
environmental protection works are shown in Figure 2.2. Key
personnel and contact particulars are summarized in Table 2.3:
Table 2.3 Contact Details of Key Personnel
Party |
Role |
Post |
Name |
Contact
No. |
Contact
Fax |
AECOM |
Engineer’s Representative for
WDII |
Principal Resident Engineer |
Mr. Frankie Fan |
2587 1778 |
2587 1877 |
Engineer’s Representative for CWB |
Principal Resident Engineer |
Mr. Peter Poon |
3912 3388 |
3912 3010 |
|
Chun Wo – Leader Joint Venture |
Contractor under Contract no. HK/2009/01 |
Project
Manager |
Mr. Simon Liu |
9304 8355 |
2587 1878 |
Site Agent |
Mr. Andy Yu |
9648 4896 |
|||
Engineer
Manager |
Mr. Terry
Wong |
9757 9846 |
|||
Construction
Manager |
Mr. Wyman
Wong |
9627 2467 |
|||
Construction
Manager |
Mr. Kenneth
Chan |
9160 3850 |
|||
Environmental Officer |
Ms. Wendy Ng |
9803 0057 |
|||
Assistant
Environmental Engineer |
Miss.
Connie Chan |
6157 7057 |
|||
Chun Wo – CRGL Joint Venture |
Contractor under Contract no. HK/2009/02 |
Project
Manager |
Mr. Paul Yu |
3658 3085 |
2827 9996 |
Quality & Environmental Manager |
Mr. C.P. Ho |
9191 8856 |
|||
China State Construction Engineering (HK) Ltd. |
Contractor under Contract no. HY/2009/15 |
Project Director |
Chris Leung |
3557 6393 |
2566 2192 |
Site Manager |
Y Huo |
3557 6368 |
|||
Contractor’s Representative |
Rex Lau |
3557 6405 |
|||
|
|
Contractor’s Representative |
Gene Cheung |
3557 6395 |
|
|
|
Environmental Officer |
Andy Mak |
3557 6347 |
|
Chun Wo - CRGL - MBEC Joint Venture |
Contractor under Contract no. HY/2009/19 |
Project Manager |
Rayland Lee |
3758 6788 |
2570 8013 |
Site Agent |
David Lau |
3758 8879 |
|||
Environmental Manager / Environmental Officer |
Eric Fong |
6191 9337 |
|||
Construction Manager (Marine) |
M.H. Isa |
9884 0810 |
|||
Construction Manager (Land) |
Andy Chan |
9879 4325 |
|||
Construction Manager (Land) |
Bear Ding |
6483 6198 |
|||
Operation Manager (Land) |
Yung Kwok Wah |
9834 1010 |
|||
China State- Leader JV |
Contractor under Contract no. HK/2012/08 |
Project Director |
C. N. Lai |
9106 5806 |
2877 1522 |
Project Manager |
Eddie Chung |
9189 8118 |
|
||
|
|
Site Agent |
Keith Tse |
9037 1839 |
|
Environmental Officer |
James Ma |
9130 9549 |
|
||
Environmental Supervisor |
Y. L. Ho |
9856 5669 |
|
||
China State |
Contractor under
Contract no. HY/2010/08 |
Project Director |
Chris Leung |
3467 4299 |
2566 8061 |
Project Manager |
Chan Ying Lun |
3418 3001 |
|
||
Site Agent |
Dave Chan |
3467 4277 |
|
||
|
|
Environmental Officer |
Gabriel Wong |
35576466 |
|
|
|
Environmental Supervisor |
Desmond Ho Tsz Ho |
3557 6466 |
|
Ramboll Environ Hong Kong Limited |
Independent
Environmental Checker (IEC) |
Independent Environmental Checker (IEC) |
Mr. David Yeung |
34652888 |
34652899 |
Lam Geotechnics Limited |
Environmental
Team (ET) |
Environmental Team Leader (ETL) |
Mr. Raymond Dai |
2882 3939 |
2882 3331 |
2.5.1.
During
this reporting period, the principal work activities for Contract no.
HK/2009/01 are summarized in Table 2.4.
Table
2.4 Principal Work Activities for Contract no.
HK/2009/01
June 2016 |
July 2016 |
August 2016 |
Nil |
Nil |
Nil |
2.5.2.
During
this reporting period, the principal work activities for Contract no. HK/2009/02
are summarized in Table 2.5.
Table
2.5 Principal Work Activities for Contract no.
HK/2009/02
June 2016 |
July 2016 |
August 2016 |
Nil |
Nil |
Nil |
2.5.3.
Major construction activities for Contract no.
HY/2009/15 was commenced on 10 November 2010. During this reporting period, the
principal work activities for Contract no. HY/2009/15 are summarized as below:
Table
2.6 Principal Work Activities for Contract no. HY/2009/15
June 2016 |
July 2016 |
August 2016 |
·
Reinstatement of vertical seawall at TPCWAE ·
Removal of temporary reclamation at TPCWAW |
·
Reinstatement of vertical seawall at TPCWAE ·
Removal of temporary reclamation at TPCWAW ·
Diaphragm wall cutting works at TPCWAW |
·
Reinstatement of vertical seawall at TPCWAE ·
Removal of temporary reclamation at TPCWAW ·
Diaphragm wall cutting works at TPCWAW |
2.5.4.
Contract no. HY/2009/19 was commenced on 24 March
2011. During this reporting period, the principal work activities for Contract
no. HY/2009/19 are summarized as below:
Table
2.7 Principal Work Activities for Contract no. HY/2009/19
June 2016 |
July 2016 |
August 2016 |
Nil |
Nil |
Nil |
2.5.5.
Contract no. HK/2012/08 was commenced on March 2013.
During this reporting period, the principal work activities for Contract no. HK/2012/08
are summarized as below:
Table
2.8 Principal Work Activities for Contract no. HK/2012/08
June 2016 |
July 2016 |
August 2016 |
Precast unit construction for Box 1 inside Dry dock
Construction of culvert L Bay 8, Bay 12 and Bay 13 |
Precast unit construction for Box 1 inside Dry dock
Construction of culvert L Bay 8, Bay 12 and Bay 13 |
Precast unit construction for Box 1
inside Dry dock Construction of culvert L Bay 8, Bay 12 and Bay 13 |
2.5.6.
Contract no. HY/2010/08 was commenced on 21 March
2013. During this reporting period, the principal work activities for Contract
no. HY/2010/08 are summarized as below:
Table 2.9 Principal Work Activities for Contract no.
HY/2010/08
June 2016 |
July 2016 |
August 2016 |
Diversion pipe maintenance
Diaphragm Wall Removal Works |
Diversion pipe maintenance
Diaphragm Wall Removal Works |
Diversion pipe maintenance
Diaphragm Wall Removal Works |
2.5.7.
Implementation
status of the recommended mitigation measures during this reporting period is
presented in Appendix 2.1.
Noise Monitoring Stations
3.1.1. The noise monitoring stations for the Project
are listed and shown in Table 3.1 and Figure 3.1. Appendix 3.1 shows the established Action/Limit
Levels for the monitoring works.
Table
3.1 Noise Monitoring Stations
Station |
Description |
M1a |
Harbour Road Sports Centre |
M2b |
Noon Gun Area |
M3a |
Tung Lo Wan Fire
Station |
M4b |
Victoria Centre |
M5b |
City Garden |
M6 |
HK Baptist Church
Henrietta Secondary School |
Noise Monitoring
Parameters, Frequency and Duration
3.1.2. The construction noise level
shall be measured in terms of the A-weighted equivalent continuous sound pressure level (Leq).
Leq (30 minutes) shall be used as the monitoring parameter for the
time period
between 0700 and 1900 hours on normal weekdays. For all other time periods, Leq
(5 minutes) shall be employed for comparison with the Noise Control
Ordinance (NCO) criteria.
Supplementary information for data auditing, statistical results such as L10
and L90 shall also be obtained for reference.
3.1.3. Noise monitoring shall be
carried out at all the designated monitoring stations. The monitoring frequency
shall depend on the scale of the construction activities. The following is an
initial guide on the
regular monitoring frequency for each station on a weekly basis when noise
generating activities are underway:
·
one
set of measurements between 0700 and 1900 hours on normal weekdays.
3.1.4. If construction works are extended to include works
during the hours of 1900 – 0700 as well as public holidays and Sundays,
additional weekly impact monitoring shall be carried out during respective
restricted hours periods. Applicable permits under NCO shall be obtained by the
Contractor.
3.1.5. Real time noise shall be carried out at the
designated monitoring stations. The following is an initial guide on the
regular monitoring frequency for each station on a 24 hours daily basis when
noise generating activities are underway:
·
One
set of measurements between 0700 and 1900 hours on normal weekdays.
·
One
set of measurements between 1900 and 2300 hours on normal weekdays and 0700 and
2300 hours on public holidays.
·
One
set of measurements between 2300 and 0700 hours on next day on everyday.
Monitoring Equipment
3.1.6. As
referred to in the Technical Memorandum ™ issued under the NCO, sound level
meters in compliance with the International Electrotechnical Commission
Publications 651: 1979 (Type 1) and 804: 1985 (Type 1) specifications shall be
used for carrying out the noise monitoring. Immediately prior to and following
each noise measurement the accuracy of the sound level meter shall be checked
using an acoustic calibrator generating a known sound pressure level at a known
frequency. Measurements may be accepted as valid only if the calibration level
from before and after the noise measurement agree to within 1.0 dB.
3.1.7. Noise
measurements shall not be made in fog, rain, wind with a steady speed exceeding
5 m/s or wind with gusts exceeding 10 m/s. The wind speed shall be checked with
a portable wind speed meter capable of measuring the wind speed in m/s.
Air Quality Monitoring
Stations
3.2.1.
The
air monitoring stations for the Project are listed and shown in Table
3.2 and Figure 3.1. Appendix 3.1 shows the established Action/Limit Levels for the
monitoring works.
Table 3.2 Air Monitoring Stations
Station ID |
Monitoring
Location |
Description |
CMA1b |
Oil Street Site
Office** |
North Point |
CMA2a |
Causeway Bay Community
Centre |
Causeway Bay |
CMA3a |
CWB PRE Site Office * |
Causeway Bay |
CMA4a |
Society for the
Prevention of Cruelty to Animals |
Wan Chai |
CMA5b |
Pedestrian Plaza*** |
Wan Chai |
CMA6a |
WDII PRE Site Office * |
Wan Chai |
Remarks*: As per the ENPC
meeting in January 2011, the monitoring stations CMA3a - Future CWB site office
at Wanchai Waterfront Promenade and CMA6a - Future AECOM site office at Work
Area were renamed as remark.
Remarks**: The location ID of monitoring station
CMA1b was updated as “Oil Street Site Office” in April 2013.
Remarks***:
The station ID and monitoring location was updated in December 2014 with
respect to monitoring station relocation.
Air Monitoring Parameters,
Frequency and Duration
3.2.2.
One-hour
and 24-hour TSP levels should be measured to indicate the impacts of
construction dust on air quality. The 24-hour TSP levels shall be measured by
following the standard high volume sampling method as set out in the Title 40
of the Code of Federal Regulations, Chapter 1 (Part 50), Appendix B.
3.2.3.
All
relevant data including temperature, pressure, weather conditions, elapsed-time
meter reading for the start and stop of the sampler, identification and weight
of the filter paper, and any other local atmospheric factors affecting or
affected by site conditions, etc., shall be recorded down in detail.
3.2.4.
For
regular impact monitoring, the sampling frequency of at least once in every
six-days, shall be strictly observed at all the monitoring stations for 24-hour
TSP monitoring. For 1-hour TSP monitoring, the sampling frequency of at least
three times in every six-days should be undertaken when the highest dust impact
occurs.
Sampling Procedure and
Monitoring Equipment
3.2.5 High
volume samplers (HVSs) in compliance with the following specifications shall be
used for carrying out the 1-hour and 24-hour TSP monitoring:
·
0.6
- 1.7 m3 per minute adjustable flow range;
·
equipped
with a timing / control device with +/- 5 minutes accuracy for 24 hours
operation;
·
installed
with elapsed-time meter with +/- 2 minutes accuracy for 24 hours operation;
·
capable
of providing a minimum exposed area of 406 cm2;
·
flow
control accuracy: +/- 2.5% deviation over 24-hour sampling period;
·
equipped
with a shelter to protect the filter and sampler;
·
incorporated
with an electronic mass flow rate controller or other equivalent devices;
·
equipped
with a flow recorder for continuous monitoring;
·
provided
with a peaked roof inlet;
·
incorporated
with a manometer;
·
able
to hold and seal the filter paper to the sampler housing at horizontal
position;
·
easily
changeable filter; and
·
capable
of operating continuously for a 24-hour period.
3.2.6 Initial
calibration of dust monitoring equipment shall be conducted upon installation
and thereafter at bi-monthly intervals. The transfer standard shall be
traceable to the internationally recognized primary standard and be calibrated
annually. The concern parties such as IEC shall properly document the
calibration data for future reference. All the data should be converted into
standard temperature and pressure condition.
Laboratory Measurement /
Analysis
3.2.7 A clean
laboratory with constant temperature and humidity control, and equipped with
necessary measuring and conditioning instruments to handle the dust samples
collected, shall be available for sample analysis, and equipment calibration
and maintenance. The laboratory should be HOKLAS accredited.
3.2.8 An
alternative non-HOKLAS
accredited laboratory was set-up for carrying out the laboratory
analysis, the laboratory equipment was approved by the ER on 8
February 2011 and
the measurement procedures were witnessed by the IEC. Any measurement performed by
the laboratory was be demonstrated to the satisfaction of the ER and IEC. IEC shall
regularly audit to the measurement performed by the laboratory to ensure the
accuracy of measurement results.
3.2.9 Filter
paper of size 8" x 10" shall be labelled before sampling. It shall be
a clean filter paper with no pinholes, and shall be conditioned in a
humidity-controlled chamber for over 24-hours and be pre-weighed before use for
the sampling.
3.2.10 After
sampling, the filter paper loaded with dust shall be kept in a clean and
tightly sealed plastic bag. The filter paper shall then be returned to the
laboratory for reconditioning in the humidity controlled chamber followed by
accurate weighing by an electronic balance with readout down to 0.1 mg. The
balance shall be regularly calibrated against a traceable standard.
3.2.11 All the
collected samples shall be kept in a good condition for 6 months before
disposal.
impact monitoring for
odour patrol
3.2.12 Odour patrols along the
shorelines of Causeway Bay Typhoon Shelter and ex-Wan Chai Public Cargo Working
Area when there is temporary reclamation in Causeway Bay Typhoon Shelter and/or in the ex-Wan Chai Public Cargo
Working Area, or when there is dredging of the odorous sediment and slime at
the south-western corner of the Causeway Bay Typhoon Shelter. Odour patrols
will be carried out at bi-weekly intervals during July, August and September by
a qualified person of the ET who shall:
·
be
at least 16 years of age;
·
be
free from any respiratory illnesses; and
·
not
be allowed to smoke, eat, drink (except water) or use chewing gum or sweets 30
min
·
before
and during odour patrol
3.2.13 Odour patrol shall be conducted by independent
trained personnel / competent persons patrolling and sniffing around the shore
as shown in Figure 3.1 to detect any odour at
the concerned hours (afternoon is preferred for higher daily temperature).
3.2.14 The qualified person will use the nose (olfactory
sensor) to sniff odours at different locations. The main odour emission sources
and the areas to be affected by the odour nuisance will be identified.
3.2.15 The perceived odour intensity is to be divided into
5 levels which are ranked in the descending order as follows:
·
0 -
Not detected. No odour perceived or an odour so weak that it cannot be easily
characterized or described;
·
1 -
Slight Identifiable odour, and slight chance to have odour nuisance;
·
2 -
Moderate Identifiable odour, and moderate chance to have odour nuisance;
·
3 -
Strong Identifiable, likely to have odour nuisance;
·
4 -
Extreme Severe odour, and unacceptable odour level.
3.2.16 The findings including odour intensity, odour
nature and possible odour sources, and also the local wind speed and direction
at each location will be recorded. In addition, some relevant meteorological
and tidal data such as daily average temperature, and daily average humidity,
on that surveyed day will be obtained from the Hong Kong Observatory Station
for reference. The Action and Limit levels for odour patrol are shown in Appendix 3.1.
3.3.1. The EIA Report has identified that the key water
quality impact would be associated with the dredging works during the
construction phase. Marine water quality
monitoring for dissolved oxygen (DO), suspended solid (SS) and turbidity is
therefore recommended to be carried out at selected WSD flushing water
intakes. The impact monitoring should be
carried out during the proposed dredging works to ensure the compliance with
the water quality standards.
3.3.2. The
updated EM&A Manual for EP-356/2009 (Version in March 2011) is approval by
EPD on 29 April 2011. As such, the Action Level and Limit Level for the wet
season (April – September) will be effected and applied to the water quality
monitoring data from 30 April 2011.
Water Quality Monitoring Stations
3.3.3. Water quality monitoring was undertaken at WSD salt
water intakes and cooling water intakes along the seafront of the Victoria
Harbour. The proposed water quality
monitoring stations of the Project are shown in Table 3.3 and Figure 3.1. Appendix 3.1 shows the established
Action/Limit Levels for the monitoring works.
Table
3.3
Marine Water Quality Stations for Water
Quality Monitoring
Station Ref. |
Location |
Easting |
Northing |
WSD Salt Water Intake |
|||
WSD19 |
Sheung Wan |
833415.0 |
816771.0 |
Cooling Water Intake |
|||
C1 |
HKCEC Extension |
835885.6 |
816223.0 |
C7 |
Windsor House |
837193.7 |
816150.0 |
P1 |
HKCEC
Phase I |
835774.7 |
816179.4 |
P3 |
The Academy of performing Arts |
835824.6 |
816212.0 |
P4 |
Shui on Centre |
835865.6 |
816220.0 |
P5 |
Government
Buildings (Wanchai
Tower / Revenue Tower / Immigration Tower) |
835895.2 |
816215.2 |
Cooling Water Intake / WSD Salt Water Intake |
|||
RW21-P789 |
Great
Eagle Centre/ Sun Hung Kai Centre/ WSD Wanchai salt water intake |
836268.0 |
816020.0 |
Remarks: - The cessation of seawater intake
operation for C6 was confirmed on 17 May 2011, the water monitoring at C6 was
then terminated since 17 May 2011.
-
4-week post construction water quality
monitoring at WSD9, WSD10, WSD15, WSD17, C8 and C9 were completed on 6 Feb 2012
and the water quality monitoring at WSD 10 and WSD15 were temporary suspended
since 8 Feb 2012, and WSD9 and WSD17 was implemented with respect to HK/2009/02
from 8 Feb 2012 onwards.
-
C8 and C9 were
implemented with respect to HY/2009/19 from 28 Jan 2012.
-
C8 & C9 were
temporary suspended since 30 March 2013.
-
WSD7 and WSD20 water
quality monitoring were temporarily suspended from 27 Apr 2012.
-
C2, C3 C4e and C4w
water quality monitoring station was temporarily suspended since 24 Apr 2013
-
C5e and C5w water
quality monitoring station was temporarily suspended since 29 July 2013.
-
WSD21 water quality
monitoring station was temporarily suspended since 12 March 2014
-
WSD9 and WSD17 water
quality monitoring station was temporarily suspended since 8 September 2014
flood tide.
-
The water quality monitoring station C1 shall
be associated with Contract No. HK/2009/02 upon commencement of marine works
under DP3 at WCR3 area
Water Quality Parameters
and frequency
3.3.4. Monitoring of dissolved oxygen (DO), turbidity and
suspended solids (SS) shall be carried out at WSD flushing water intakes and
cooling water intakes. DO and Turbidity are measured in-situ while SS is
determined in laboratory.
3.3.5. In association with the water quality parameters,
other relevant data shall also be measured, such as monitoring
location/position, time, sampling depth, water temperature, pH, salinity,
dissolved oxygen (DO) saturation, weather conditions, sea conditions, tidal
stage, and any special phenomena and work underway at the construction site
etc.
3.3.6. The interval between two sets of monitoring should
not be less than 36 hours except where there are exceedances of Action and/or
Limit Levels, in which case the monitoring frequency will be increased. Table 3.4 shows the proposed
monitoring frequency and water quality parameters. Duplicate in-situ measurements and water
sampling should be carried out in each sampling event. For selection of tides for in-situ
measurement and water sampling, tidal range of individual flood and ebb tides
should be not less than 0.5m.
Table
3.4 Marine Water Quality Monitoring Frequency
and Parameters
Activities |
Monitoring Frequency1 |
Parameters2 |
During the 4-week
baseline monitoring period |
Three days per week,
at mid-flood and mid-ebb tides |
Turbidity, Suspended
Solids (SS), Dissolved Oxygen (DO), pH, Temperature, Salinity |
During marine construction works |
Three days per week,
at mid-flood and mid-ebb tides |
Turbidity, Suspended
Solids (SS), Dissolved Oxygen (DO), pH, Temperature, Salinity |
After completion of marine construction works |
Three days per week,
at mid-flood and mid-ebb tides |
Turbidity, Suspended
Solids (SS), Dissolved Oxygen (DO), pH, Temperature, Salinity |
Notes:
1. For
selection of tides for in-situ measurement and water sampling, tidal range of
individual flood and ebb tides should be not less than 0.5m.
2.
Turbidity should be
measured in situ whereas SS should be determined by laboratory.
Dissolved Oxygen and
Temperature Measuring Equipment
3.3.7. The instrument should be a portable, weatherproof
dissolved oxygen measuring instrument complete with cable, sensor,
comprehensive operation manuals, and use a DC power source. It should be
capable of measuring:
·
a
dissolved oxygen level in the range of 0-20 mg/l and 0-200% saturation
·
a
temperature of 0-45 degree Celsius
3.3.8. It should have a membrane electrode with automatic
temperature compensation complete with a cable. Sufficient stocks of spare
electrodes and cables should be available for replacement where necessary.
(e.g. YSI model 59 meter, YSI 5739 probe, YSI 5795A submersible stirrer with
reel and cable or an approved similar instrument).
3.3.9. Should salinity compensation not be build-in in the
DO equipment, in-situ salinity shall be measured to calibrate the DO equipment
prior to each DO measurement.
Turbidity Measurement
Instrument
3.3.10 The
instrument should be a portable, weatherproof turbidity-measuring instrument
complete with comprehensive operation manual. The equipment should use a DC
power source. It should have a photoelectric sensor capable of measuring
turbidity between 0‑1000 NTU and be complete with a cable (e.g. Hach
model 2100P or an approved similar instrument).
Sampler
3.3.11 Water sampler comprises a transparent PVC
cylinder, with a capacity of not less than 2 litres, and can be effectively
sealed with latex cups at both ends. The sampler should have a positive
latching system to keep it open and prevent premature closure until released by
a messenger when the sampler is at the selected water depth (e.g. Kahlsico
Water Sampler or an approved similar instrument).
Sample Container and
Storage
3.3.12 Water
samples for suspended solids measurement should be collected in high-density
polythene bottles, packed in ice (cooled to 4°C without being frozen), and
delivered to ALS Technichem (HK) Pty Ltd. as soon as possible after collection
for analysis.
Water Depth Detector
3.3.13 A
portable, battery-operated echo sounder shall be used for the determination of
water depth at each designated monitoring station. This unit can either be
handheld or affixed to the bottom of the workboat, if the same vessel is to be
used throughout the monitoring programme.
Salinity
3.3.14 A portable
salinometer capable of measuring salinity in the range of 0-40 ppt shall be
provided for measuring salinity of the water at each of monitoring location.
Monitoring Position
Equipment
3.3.15 A
hand-held or boat-fixed type digital Global Positioning System (GPS) with
waypoint bearing indication or other equivalent instrument of similar accuracy
shall be provided and used during monitoring to ensure the monitoring vessel is
at the correct location before taking measurements.
Calibration of In-situ
Instruments
3.3.16 All
in-situ monitoring instrument shall be checked, calibrated and certified by a
laboratory accredited under HOKLAS or equivalent before use, and subsequently
re-calibrated at 3 monthly intervals throughout all stages of the water quality
monitoring. Responses of sensors and electrodes should be checked with
certified standard solutions before each use. Wet bulb calibration for a DO
meter shall be carried out before measurement at each monitoring location.
3.3.17 For the on
site calibration of field equipment by the ET, the BS 127:1993, "Guide to
Field and on-site test methods for the analysis of waters" should be
observed.
3.3.18 Sufficient
stocks of spare parts should be maintained for replacements when necessary.
Backup monitoring equipment shall also be made available so that monitoring can
proceed uninterrupted even when some equipment is under maintenance,
calibration, etc.
Laboratory Measurement /
Analysis
3.3.19 Analysis
of suspended solids has been carried out in a HOKLAS accredited laboratory, ALS
Technichem (HK) Pty Ltd. Water samples of about 1L shall be collected at the
monitoring stations for carrying out the laboratory SS determination. The SS
determination work shall start within 24 hours after collection of the water
samples. The SS determination shall follow APHA 19ed or equivalent methods
subject to the approval of IEC and EPD.
Enhanced Water Quality
Monitoring in the ex-Wan Chai Public Cargo
Working Area and the
Causeway Bay Typhoon Shelter
3.3.20 The
enhanced water quality monitoring and audit programme is to avoid aggravation
of odour nuisance from seawater arising from temporary reclamation in the
ex-Wan Chai Public Cargo Working Area and the Causeway Bay Typhoon Shelter.
3.3.21 Dissolved
oxygen monitoring at the intakes C6 and C7 in Causeway Bay Typhoon Shelter when
there is temporary reclamation in Causeway Bay Typhoon Shelter and at the south-western
and south-eastern corners of the ex-Wan Chai Public Cargo Working Area. The
proposed water quality monitoring stations of the Project are shown in Table
3.5 and Figure 3.1.
Table 3.5 Marine
Water Quality Stations for Enhanced Water Quality Monitoring
Station |
Location |
C6 |
Excelsior Hotel |
C7 |
Windsor House |
Ex-WPCWA-SW |
South-western of the ex-Wan Chai
Public Cargo Working Area |
Ex-WPCWA-SE |
South-eastern of the ex-Wan Chai
Public Cargo Working Area |
Remarks:
1.
Enhanced DO monitoring at Windsor House Cooling
(Station Ref: C7) was temporarily suspended since 22 October 2014 with respect
to the formation of temporary reclamation zone TS3 and to be resumed upon
removal of the respective temporary reclamation zone.
2.
Enhanced DO monitoring at Monitoring station at
Ex-PCWAE was temporarily suspended from 31 August 2015 with respect to seawall
reinstatement works and formation of active works area, to be resumed upon
completion of seawall reinstatement works
3.3.22 The
monitoring of dissolved oxygen are to be carried out 3 days per week, at
mid-flood and mid-ebb tides for 3 water depths (1m below water surface,
mid-depth and 1m above sea bed, except where the water depth less than 6m, the mid-depth
may be omitted. If the water depth be less than 3m, only the mid-depth will be
monitored).
Daily SS Monitoring and 24
hours Turbidity Monitoring System
3.3.23 During
dredging of the sediment at the south-western corner of the Causeway Bay
Typhoon Shelter, daily monitoring of suspended solids and 24 hour monitoring of
turbidity at the cooling water intakes (C6 and C7) shall be conducted.
3.3.24 The 24
hours monitoring of turbidty at the cooling water intakes (C6 and C7) shall be
established by setting up a continuous water quality monitoring station in
front of the intakes during the dredging activities. The monitoring system include the turbidity
sensor and data logger which is capable of data capturing at every 5 minutes.
The data shall be downloaded daily and compared with the Action and Limit level
determined during the baseline water qualtiy monitoring at the cooling water
intake locations.
Additional Dissovled
oxygen Monitoring FOR CULVERT L WATER DISCHARGE FLOW
3.3.25 In
response to the Condition 2.18 of the Environmental Permit no. EP-356/2009
requiring that a silt curtain / impermeable barrier system be installed to
channel water discharge flow from Culvert L to locations outside the embayment
area, a proposed replacement of the requirement with additional dissolved
oxygen monitoring has been conducted at three monitoring stations, namely A, B
and C between the eastern seawall of Central Reclamation Phase III and the
HKCEC Extension since November 2011 under EP-356/2009 so that DO level between
the eastern seawall of Central Reclamation Phase II and the HKCEC extension
could be continuously monitored.
3.3.26 With
respect to the commencement of dredging works under HK/2012/08 and the
installation of MTR precast protection unit, the enhanced water quality
monitoring for Culvert L was temporarily suspended since 24 July 2013
3.3.27 The
monitoring of dissolved oxygen are to be carried out once per week, at
mid-flood and mid-ebb tides for 3 water depths (1m below water surface,
mid-depth and 1m above sea bed, except where the water depth less than 6m, the
mid-depth may be omitted. If the water depth be equal to or less than 3m, only
the mid-depth will be monitored).
4.0.1. The environmental monitoring will be implemented
based on the division of works areas of each designed project managed under
different contracts with separate FEP applied by individual contractors. Overall layout showing work areas of various
contracts, latest status of work commencement and monitoring stations is shown
in
Figure
2.1 and Figure
3.1. The monitoring results are presented in according to the
Individual Contract(s).
4.0.2 According to
EP-364/2009/A Part B, “Scale and Scope of Designated Project”, Remarks (c),”The
permanent and temporary reclamation and associated dredging works related to
the CWB construction are separately covered by environmental permit No.
EP-356/2009 issued to Civil Engineering and Development Department”, and
marine piling works to be conducted by the Contractor of Contract no. HY/2009/19
from 28 January 2012 was considered to be governed under EP-356/2009. As the
construction site area of Contract no. HY/2009/11 had already been handed over
to Contract no. HY/2009/19, the designated noise, water and air quality
monitoring stations for Contract no. HY/2009/11 would be shared with Contract
no. HY/2009/19 from 28 January 2012.
Contract no. HK/2009/01 - Wan Chai Development
Phase II – Central –Wanchai Bypass at HKCEC and Contract no. HK/2009/02 - Wan
Chai Development Phase II – Central – Wan Chai Bypass at WanChai East
4.1.1.
The
proposed divisions of noise monitoring stations are summarized in Table
4.1 below.
Table 4.1 Noise Monitoring Station for Contract nos. HK/2009/01 and HK/2009/02
Station |
Description |
M1a |
Harbour Road Sports Centre |
4.1.2. Three limit level exceedances were
recorded at M1a- Harbour Road Sports Centre on 7, 13 and 21 June 2016 in June
reporting month.
4.1.3.
Operation of Hydromil Trench Cutter at Ex-Wan Chai Swimming Pool
(adjacent to Harbour Road Sports Centre directly opposite to the monitoring
station) under non WDII-CWB Contractor as major noise contribution during
monitoring on 7 and 13 June 2016. As such, the exceedances were considered as
non-Project related.
4.1.4. Breaking work at Ex-Wan Chai Swimming
Pool (adjacent to Harbour Road Sports Centre directly opposite to the
monitoring station) under non WDII-CWB Contractor was observed as the major
noise contribution during monitoring on 21 June 2016. As such, the exceedance
was considered as non-Project related.
4.1.5. One limit level exceedances was recorded
at M1a- Harbour Road Sports Centre on 28 June 2016 in July reporting month.
4.1.6. Operation of drill rig at opposite to
the monitoring station under non WDII-CWB Contractor was observed as the major
noise contribution during monitoring on 28 June 2016. As such, the exceedances
were considered as non-Project related.
4.1.7. No action or limit level exceedance was
recorded in August reporting month.
Contract no. HY/2009/15 - Central-Wanchai Bypass – Tunnel (Causeway Bay
Typhoon Shelter Section)
4.1.8. The noise monitoring for HY/2009/15 was
commenced on 10 November 2010. The
proposed division of noise monitoring stations are summarized in Table
4.2 below.
Table
4.2
Noise Monitoring Station for Contract nos. HY/2009/15
Station |
Description |
M2b |
Noon Gun Area |
M3a |
Tung Lo Wan Fire Station |
4.1.9.
No action
or limit level exceedance was recorded in this report quarter.
Contract no. HY/2009/19 – Central- Wan Chai Bypass
Tunnel (North Point Section) and Island Eastern Corridor Link
4.1.10.
Noise
quality monitoring at M4b and M5b have been implemented with respect to
HY/2009/19 since the marine bore piling work started on 28 Jan 2012.
4.1.11.
The
proposed division of noise monitoring stations for Contract no. HY/2009/19 are
summarized in Table 4.3 below:
Table 4.3
Noise Monitoring
Stations for Contract no. HY/2009/19
Station |
Description |
M4b |
Victoria Centre |
M5b |
City Garden |
M6 |
HK Baptist Church Henrietta Secondary School |
4.1.12.
School examination was scheduled to be taken place at Henrietta
Secondary School on 06 June 2016 to 22 June 2016, the limit level of noise
monitoring at station M6 was adjusted to 65dB(A) during examination period
accordingly.
4.1.13. Three limit level exceedances were
recorded at M6 – HK Baptist Church Henrietta Secondary School on 7, 13 and 21
June 2016 in June reporting month.
4.1.14.
No construction work was conducted during the time of measurement on 7
and 13 June 2016, and it was observed that traffic noise was a major noise
source during monitoring. It is concluded that the exceedance was not due to
project but to traffic noise nearby.
4.1.15.
Only rebar fixing and shifting of launching girder for segment placing
were conducted around the monitoring location on 21 June 2016 and nearby
traffic noise was observed as major noise source during monitoring. In
addition, external wall renovation at City Garden was observed. In view of the
above, the exceedance was considered as non-Project related.
4.1.16. One limit level exceedance was recorded
at M6- HK Baptist Church Henrietta Secondary School on 12 July 2016 in July
reporting month.
4.1.17.
Traffic noise was observed during monitoring on 12 July 2016 and it was
considered as the major noise contribution. As such, the limit level exceedance
was concluded as non-project related.
4.1.18.
No action or limit level exceedance was recorded in August reporting
month.
Contract
no. HY/2010/08-Central-Wanchi Bypass Tunnel (Slip Road 8 Section)
4.1.19.
The proposed division of noise monitoring stations
are summarized in Table 4.4 below.
Table 4.4 Noise Monitoring Station for Contract no. HY/2010/08
Station |
Description |
M2b |
Noon Gun Area |
M3a |
Tung Lo Wan Fire Station |
4.1.20.
No action or limit level exceedance was recorded in the reporting
quarter.
4.1.21.
All Noise monitoring results measured in this
reporting period are reviewed and summarized. Details of noise monitoring
results and graphical presentation can be referred in Appendix 4.1.
4.3.1.
1hr and 24hr TSP monitoring were conducted at CMA1b,
CMA2a, CMA3a, CMA4a, CMA5b and CMA6a in the reporting period.
Contract no. HK/2009/01 - Wan Chai Development
Phase II – Central –Wanchai Bypass at HKCEC
4.3.2.
Air
monitoring was commenced on 1 April 2011 in response to the commencement of the
land-filling work for Contract no. HK/2009/01. The proposed division of air
monitoring stations are summarized in Table 4.5 below.
Table
4.5 Air Monitoring Stations for Contract no. HK/2009/01
Station |
Description |
CMA5b |
Pedestrian Plaza |
CMA6a |
WDII PRE Site Office * |
4.3.3. No action
or limit level exceedance was recorded in this reporting quarter.
Contract no. HK/2009/02 - Wan Chai Development
Phase II – Central – Wan Chai Bypass at WanChai East
4.3.4.
Air
monitoring was commenced in mid-January 2011 for the land-filling work for
Contract no. HK/2009/02. The proposed division of air monitoring stations is
summarized in Table 4.6 below.
Table
4.6 Air Monitoring Station
for Contract no. HK/2009/02
Station |
Description |
CMA4a |
Society for the Prevention of Cruelty to Animals |
4.3.5.
No
action or limit level exceedance was recorded in this reporting quarter.
Contract no. HY/2009/15 - Central-Wanchai Bypass – Tunnel (Causeway Bay
Typhoon Shelter Section)
4.3.6.
Air
monitoring was commenced on 15 March 2011 for the land filling work for
Contract no. HY/2009/15. The proposed division of air monitoring
stations are summarized in Table 4.7 below.
Table 4.7
Air
Monitoring Station for Contract no. HY/2009/15
Station |
Description |
CMA3a |
CWB PRE Site Office |
4.3.7. No action
or limit exceedance was recorded in this reporting quarter.
4.3.8. The odour patrol along the odour route
with 7 sniffing locations was conducted by a qualified odour patrol member on 5
July 2016 and 20 July 2016 at the concerned hours (afternoon for higher daily
temperature). No action and limit level was recorded during July reporting
month.
4.3.9. The odour patrol along the odour route
with 7 sniffing locations was conducted by a qualified odour patrol member on 1
August 2016 and 17 August 2016 at the concerned hours (afternoon for higher
daily temperature). No action and limit level was recorded during August
reporting month.
Contract no. HY/2009/19 –Central- Wan Chai Bypass
Tunnel (North Point Section) and Island Eastern Corridor Link
4.3.10.
Air monitoring at CMA1b and CMA2a have been
implemented with respect to HY/2009/19 since the marine bore piling works
started on 28 Jan 2012. No exceedance was recorded in the reporting
period.
4.3.11.
The proposed division of air monitoring stations is
summarized in Table 4.8 below.
Table
4.8 Air
Monitoring Stations for Contract no. HY/2009/19
Station |
Description |
CMA1b |
Oil Street Site Office |
CMA2a |
Causeway Bay Community Centre |
4.3.12.
No action or limit level exceedance was recorded
in June reporting month.
4.3.13.
No action or limit level exceedance was recorded
in July reporting month.
4.3.14.
One 1hr TSP action level exceedance was recorded on 27 August 2016 in
August reporting month.
4.3.15. No construction works was undertaken on
the monitoring date at around Oil Street Site Office. Dust suppression measure
including haul road maintained in dampened condition was implemented and no
particular observation regarding air quality impact was observed during
sampling. In view of the above, the action level exceedance was considered to
be non-project related and contributed by local ambient condition.
Contract no. HK/2012/08- Wan Chai Development Phase
II – Central-Wan Chai Bypass at Wan Chai West
4.3.16.
The proposed division of air monitoring stations are summarized in Table
4.9 below.
Table 4.9 Air Monitoring Stations
for Contract no. HK/2012/08
Station |
Description |
CMA5b |
Pedestrian Plaza |
4.3.17.
No action or limit level exceedance was recorded in this reporting quarter.
Contract no. HY/2010/08- Central-Wanchai Bypass
Tunnel (Slip Road 8 Section)
The proposed division of air
monitoring stations are summarized in Table 4.10 below.
Table 4.10 Air Monitoring
Stations for Contract no. HY/2010/08
Station |
Description |
CMA3a |
CWB PRE Site Office |
4.3.18. No action or limit level
exceedance was recorded in this reporting quarter.
4.3.19. The odour patrol along the odour route
with 7 sniffing locations was conducted by a qualified odour patrol member on 5
July 2016 and 20 July 2016 at the concerned hours (afternoon for higher daily
temperature). No action and limit level was recorded during July reporting
month
4.3.20. The odour patrol along the odour route
with 7 sniffing locations was conducted by a qualified odour patrol member on 1
August 2016 and 17 August 2016 at the concerned hours (afternoon for higher
daily temperature). No action and limit level was recorded during August
reporting month.
Contract no. HK/2009/01 - Wan Chai Development
Phase II – Central –Wanchai Bypass at HKCEC
4.4.1.
Water quality monitoring for Contract no. HK/2009/01 was
commenced on 23 July 2010. The proposed division of water monitoring stations
is summarized in Table 4.11 below.
4.4.2.
Water quality monitoring station RW21-P789 has been
implemented with respect to HK/2009/02 started on 29 July 2013.
Table 4.11 Water Monitoring Stations for Contract no. HK/2009/01
Station
Ref. |
Location |
Easting |
Northing |
Cooling Water Intake |
|||
C1 |
HKCEC
Extension |
835885.6 |
816223.0 |
4.4.3.
No
action or limit level exceedance was recorded in this reporting quarter.
Contract no. HK/2009/02 - Wan Chai Development Wan
Chai Development Phase II – Central – Wan Chai Bypass at WanChai East
4.4.4.
Water
quality monitoring for Contract no. HK/2009/02 was commenced on 8 July 2010.
The proposed division of water monitoring stations is summarized in Table
4.12 below.
Table 4.12 Water Monitoring Stations for Contract no. HK/2009/02
Station
Ref. |
Location |
Easting |
Northing |
||
Cooling Water Intake |
|||||
C1 |
HKCEC
Extension |
835885.6 |
816223.0 |
||
Cooling Water Intake |
|||||
RW21-P789 |
Great Eagle Centre/ Sun Hung Kai Centre/WSD Wanchai salt
water intake / China Resources Building |
836268.0 |
816020.0 |
||
4.4.5.
No action or limit level exceedance was recorded in this reporting
quarter.
Contract
no. HK/2012/08 - Wan Chai Development Phase II – Central- Wan Chai Bypass at Wan
Chai West
4.4.6.
Water
monitoring for Contract no. HK/2012/08 was commenced on 5 March 2013. The
proposed division of water monitoring stations are summarized in Table 4.13
below.
Table 4.13
Water Monitoring Stations for Contract
no. HK/2012/08
Station
Ref. |
Location |
Easting |
Northing |
|
WSD Salt Water Intake |
||||
WSD19 |
Sheung Wan |
833415.0 |
816771.0 |
|
Cooling Water Intake |
||||
P1 |
HKCEC Phase I |
835774.7 |
816179.4 |
|
P3 |
The Academy of
performing Arts |
835824.6 |
816212.0 |
|
P4 |
Shui on Centre |
835865.6 |
816220.0 |
|
P5 |
Government Buildings (Wanchai Tower /
Revenue Tower / Immigration Tower) |
835895.2 |
816215.2 |
|
4.4.7. No action or limit level exceedance was
recorded in June reporting month.
4.4.8. No action or limit level exceedance was
recorded in July reporting month.
4.4.9. There was 1 action level turbidity
exceedance recorded at P5 on 19 August 2016 in August reporting month.
4.4.10. After checking with the Contractor, no
marine activity was conducted on the monitoring date. Location of construction
area was at downstream of monitoring station P5. In view of the above, and no
exceedance was recorded on the subsequent monitoring, the exceedance was
considered not project related.
Contract no.
HY/2009/15 - Central-Wanchai Bypass – Tunnel (Causeway Bay Typhoon Shelter
Section)
4.4.11.
Due to the commencement of the
maintenance dredging on 10 November 2010, water quality monitoring for Contract
no. HY/2009/15 was commenced on 9 November 2010. The proposed division of water
monitoring stations is
summarized in Table 4.14 and Table 4.15 below.
Table 4.14 Water Monitoring Stations for Contract no.
HY/2009/15
Station
Ref. |
Location |
Easting |
Northing |
Cooling Water Intake |
|||
C7 |
Windsor
House |
837193.7 |
816150.0 |
Remarks: - The cessation of seawater intake operation for C6
was confirmed on 17 May 2011, the water monitoring at C6 was then terminated
since 17 May 2011.
Table 4.15
Enhance Dissolved Oxygen Monitoring Stations for Contract no. HY/2009/15
Station
Ref. |
Location |
C6 |
Excelsior
Hotel |
Ex-WPCWA SW |
South-western
of the ex-Wan Chai Public Cargo Working Area |
Remarks:
1.
Enhanced DO monitoring at Windsor House Cooling
(Station Ref: C7) was temporarily suspended since 22 October 2014 with respect
to the formation of temporary reclamation zone TS3 and to be resumed upon
removal of the respective temporary reclamation zone.
2.
Enhanced DO monitoring at Monitoring station at
Ex-PCWAE was temporarily suspended from 31 August 2015 with respect to seawall
reinstatement works and formation of active works area, to be resumed upon
completion of seawall reinstatement works
4.4.12.
There were no action and 1 limit level turbidity exceedance recorded at
C7 on 24 June 2016 and 2 action level and no limit level SS exceedances
recorded at C7 on 18 and 24 June 2016 in June reporting month.
4.4.13.
After checking with contractor, no marine activity was conducted at
Causeway Bay Typhoon Shelter on 18 and 24 June 2016. In view of no marine construction
activity, and no turbidity and SS exceedance recorded on the subsequent
monitoring, it was considered that the exceedances were not project related.
4.4.14.
There was no action and 1 limit level DO exceedance recorded at Ex-WPCWA
SE on 1 June 2016 in June reporting month.
4.4.15.
After checking with contractor, no marine activity was conducted at
TPCWAW on 1 June 2016. Upstream discharge from nearby culvert was noted. In
view of no marine activity and no exceedance was recorded on the subsequent
monitoring, the exceedance was considered not related to Project works.
4.4.16.
There were 1 action and 3 limit level DO exceedances recorded at
Ex-WPCWA SW on 10, 16, 18 and 24 June 2016 in June reporting month.
4.4.17. After checking with contractor, no
marine activity was conducted at TPCWAW on 10, 16, 18 and 24 June 2016.
Upstream discharge from nearby culvert was noted. In view of no marine
activity, the exceedance was considered not related to Project works.
4.4.18. There were 1 action and 1 limit level
turbidity exceedance recorded at C7 on 2 July 2016 and 25 July 2016 in this
July month.
4.4.19.
After checking with contractor, no marine activity was conducted at
Causeway Bay Typhoon Shelter on 2 July 2016 and 25 July 2016. In view of no
marine construction activity, and no exceedance recorded on the subsequent
monitoring, it was considered that the exceedances were not project related.
4.4.20.
There were 2 limit level DO exceedances recorded at Ex-WPCWA SW on 2
July 2016 and 4 July 2016 in July reporting month.
4.4.21.
After checking with contractor, transfer of mud from shaft B to barge
was observed conducted at Ex-PCWA during sampling on 2 July 2016 and silt
curtain was observed deployed at the outfall location of culvert O. The silt
curtain was observed partially deployed (without extending to water column) at the
outfall location of culvert O. In view of the environmental concern on
potential accumulation of organic pollutant in relate to the embayment effect
at the concerned location due to the silt curtain deployment, the contractor
was advised to remove any silt curtain/ impermeable deployed at the outfall
location of culvert O. All obstruction at the outfall location of culvert O was
subsequently removed by contractor on 5 July 2016. No further dissolved oxygen
exceedance was recorded during subsequent monitoring conducted on 4 July 2016.
Considering the upstream organic discharge influence and the partial silt
curtain deployment (without extending to water column) observed during
monitoring, the implication of the partially deployed silt curtain on the water
circulation could not concluded. Nevertheless, the contractor was advised that
any silt curtain/ impermeable barrier shall not be deployed at the culvert O
outfall location so that the water circulation would not be adversely affected.
In addition, the contractor was reminded to maintain a tarpaulin sheet between
the shaft and barge during soil material transfer to avoid potential drop off
to nearby waters and to maintain a proper deployment of silt curtain extending
throughout the water column around the derrick barge during excavated material
transfer to avoid potential muddy dispersion.
4.4.22.
Removal of steel brackets was observed conducted at Ex-PCWA during
sampling on 4 July 2016 and impermeable barrier was observed deployed at the
outfall location of culvert O. The impermeable barrier was observed partially
deployed (without extending to water column) at the outfall location of culvert
O. In view of the environmental concern on potential accumulation of organic
pollutant in relate to the embayment effect at the concerned location due to
the silt curtain deployment, the contractor was advised to remove any silt
curtain/ impermeable deployed at the outfall location of culvert O. All
obstruction at the outfall location of culvert O was subsequently removed by contractor
on 05 July 2016. No further dissolved oxygen exceedance was recorded during
subsequent monitoring conducted on 04 July 2016. Considering the upstream
organic discharge influence and the partial impermeable barrier deployment
(without extending to water column) observed during monitoring, the implication
of the partially deployed impermeable barrier on the water circulation could
not concluded. Nevertheless, the contractor was advised that any silt curtain/
impermeable barrier shall not be deployed at the culvert O outfall location so
that the water circulation would not be adversely affected.
4.4.23.
There were 1 action level DO exceedances recorded at Ex-WPCWA SE on 22
July 2016 in this July month.
4.4.24. Despite removal of diaphragm wall and
excavation by derrick barge at northern side of TPCWAW were conducted on 22
July 2016, contractor mitigation measures including the use of silt curtain was
in place. Upstream discharge from nearby culvert was noted. In view of the
above and no exceedance was recorded on the subsequent monitoring, the
exceedance was considered not related to the Project works.
4.4.25. There were 1 action level and 1 limit
level turbidity exceedance recorded at C7 on 3 and 26 August 2016 in August
reporting month.
4.4.26.
After checking with the contractor, despite mud transhipment was
conducted on 3 August 2016, contractor mitigation measures including the use of
tarpaulin sheet between two barges was generally in order. In view of the
above, the exceedance was considered not related to construction works.
4.4.27.
No marine activity was conducted at Causeway Bay Typhoon Shelter on 26
August 2016. In view of no marine construction activity, the exceedances were
considered not related to construction works.
4.4.28.
There was 11 limit level DO exceedance recorded at Ex-WPCWA SW on 29
July 2016, 1, 5, 8, 13, 15, 22, 24 and 26 August 2016 in August reporting
month.
4.4.29.
After checking with the Contractor, despite underwater excavation at
northern side of TPCWAW was conducted on 29 July 2016, contractor mitigation
measures including the use of silt curtain and impermeable barrier was in
place. Upstream discharge from nearby culvert was noted. In view of the above
and no exceedance was recorded on the subsequent monitoring, the exceedance was
considered not related to the Project works.
4.4.30.
Despite removal of diaphragm wall was conducted on 5 and 8 August 2016,
contractor mitigation measures including the use of silt curtain and
impermeable barrier was in place. Upstream discharge from nearby culvert was
noted. In view of the above, the exceedances were considered not related to the
Project works.
4.4.31.
No marine construction activity was conducted at TPCWAW on 1 and 13
August 2016. Upstream discharge from nearby culvert was noted. In view of no
marine construction activity was conducted, the exceedance was considered not
related to Project works.
4.4.32.
Despite transport of soil from land to derrick barge near Shaft B at
TPCWAW was conducted on 15 and 22 August 2016 on the monitoring date,
contractor mitigation measures including the provision of tarpaulin sheet
between land and barge and use of silt curtain was in place. Upstream discharge
from nearby culvert was noted. In view of the above, the exceedance was
considered not related to Project works.
4.4.33.
Despite removal of seawall blocks near Shaft B and removal of diaphragm
wall at Northern side of TPCWAW were conducted on 24 August 2016, contractor
mitigation measures including the use of silt curtain and impermeable barrier
were in place. Upstream discharge from nearby culvert was noted. In view of the
above, and no exceedance was recorded on the subsequent monitoring, the
exceedance was considered not related to Project works.
4.4.34.
Despite filling levelling stone for seawall reinstatement at Western
side of TPCWAW and underwater excavation works near Shaft B were conducted
under Contract HY/2009/15 on 26 August 2016, contractor mitigation measures
including the use of silt curtain and impermeable barrier were implemented.
Upstream discharge from nearby culvert was noted. In view of the above, and no
exceedance was recorded on the subsequent monitoring, the exceedance was
considered not related to Project works. Nevertheless, the Contractor of
HY/2009/15 was reminded to review the positioning of the impermeable barrier
such that the water circulation within the temporarily diverted culvert channel
would not be affected to avoid potential odour concern within the temporarily
diverted culvert channel.
4.4.35.
There were 1 action and 1 limit level DO exceedances recorded at
Ex-WPCWA SE on 5 and 8 August 2016 in August reporting month.
4.4.36. Despite removal of diaphragm wall was
conducted on 5 and 8 August 2016, contractor mitigation measures including the
use of silt curtain and impermeable barrier was in place. Upstream discharge
from nearby culvert was noted. In view of the above and no exceedance was
recorded on the subsequent monitoring, the exceedances were considered not
related to the Project works.
Contract no. HY/2010/08- Central-Wanchai Bypass
Tunnel (Slip Road 8 Section)
4.4.37. The proposed division of water
quality monitoring stations are summarized in Table 4.16 and Table
4.17 below:
Table 4.16 Water quality monitoring Stations for Contract no.
HY/2010/08
Station
Ref. |
Location |
Easting |
Northing |
Cooling Water Intake |
|||
C7 |
Windsor
House |
837193.7 |
816150.0 |
Table 4.17
Enhance Dissolved Oxygen Monitoring Stations for Contract no. HY/2010/08
Station
Ref. |
Location |
C6 |
Excelsior
Hotel |
Remarks:
1.
Enhanced DO monitoring at Windsor House Cooling
(Station Ref: C7) was temporarily suspended since 22 October 2014 with respect
to the formation of temporary reclamation zone TS3 and to be resumed upon
removal of the respective temporary reclamation zone.
1.4.1. There were no action and 1 limit level
turbidity exceedance recorded at C7 on 24 June 2016 and 2 action level and no
limit level SS exceedances recorded at C7 on 18 and 24 June 2016 in June
reporting month.
1.4.2. After checking with contractor, no
marine activity was conducted on 18 and 24 June 2016. Installed silt screen was
in place. In view of no marine construction activity, and no turbidity and SS
exceedance recorded on the subsequent monitoring, it was considered that the
exceedances were not project related.
1.4.3. There were 1 action and 1 limit level
turbidity exceedance recorded at C7 on 2 July 2016 and 25 July 2016 in July
reporting month.
1.4.4.
After checking with contractor, despite reinstate of seawall was
conducted at TS3N3 corner on 2 July 2016, contractor mitigation measure
including the deployment of silt curtain was generally in order and installed
silt screen was in place. In view of the above, and no exceedance was recorded
on the subsequent monitoring, it was considered that the exceedance was not
project related.
1.4.5. Despite placing of seawall blocks was
conducted on the monitoring date, contractor mitigation measures including the
use of silt curtain was in place and the installed silt screen was in place. In
view of the above, and no exceedance was recorded on the subsequent monitoring,
it was considered that the exceedance was not project related.
1.4.6. There were 1 action and 1 limit level
turbidity exceedance recorded at C7 on 3 and 26 August 2016 in August reporting
month.
1.4.7.
After checking with contractor, despite reinstatement of seawall at
TS3BE was conducted on 3 August 2016, contractor mitigation measures including
the use of silt curtain and impermeable barrier was in place and the installed
silt screen was in place. In view of the above, and no exceedance was recorded
on the subsequent monitoring, it was considered that the exceedance was not
project related.
1.4.8. No marine activity was conducted on 26
August 2016, and the installed silt screen was in place. In view of the above,
and no exceedance was recorded on the subsequent monitoring, it was considered
that the exceedance was not project related.
Contract no. HK/2009/01 - Wan Chai Development
Phase II – Central –Wanchai Bypass at HKCEC
4.5.1. No Inert C&D waste and
non-inert C&D waste was
disposed of for the site works in this reporting period. Details of the waste
flow table are summarized in Table 4.18.
Table 4.18 Details of Waste Disposal for Contract no. HK/2009/01
Waste Type |
Quantity this quarter |
Cumulative Quantity-to-Date |
Disposal / Dumping Grounds |
Inert C&D materials disposed, m3 |
NIL |
62116.405 |
TKO137, TM38 |
Inert C&D materials recycled, m3 |
NIL |
5856.5 |
N/A |
Non-inert C&D materials disposed, m3 |
NIL |
1673.69 |
SENT Landfill |
Non-inert C&D materials recycled, kg |
NIL |
203993 |
N/A |
Chemical waste disposed, kg |
NIL |
10250 |
N/A |
Marine Sediment (Type 1 – Open Sea Disposal)
, m3 |
NIL (Bulk Volume) |
97428.2 (Bulk Volume) |
South of Cheung Chau |
Marine Sediment (Type 1 – Open Sea Disposal
(Dedicate Sites) & Type 2 – Confined Marine Disposal) , m3 |
NIL (Bulk Volume) |
52250 (Bulk Volume) |
East of Cha Chau |
Dredged Sediment Requiring Type 3 – Special Treatment / Disposal contained in
Geosynthetic Containers |
NIL (Bulk Volume) |
6773 (Bulk Volume) |
East of Cha Chau |
4.5.2. There were no Marine Sediment (Type 1 –
Open Sea Disposal) and no Marine Sediment
(Type 1- Open Sea Disposal (Dedicate Sites) & Type 2- Confined Marine
Disposal) disposed of in this reporting quarter.
Contract no. HK/2009/02 - Wan Chai Development
Phase II – Central – Wan Chai Bypass at WanChai East
4.5.3. No Inert and non-inert C&D waste were disposed of for the
site works in this reporting period. Details of the waste flow table are
summarized in Table 4.19.
Table 4.19 Details of Waste Disposal for Contract no. HK/2009/02
Waste Type |
Quantity this quarter |
Cumulative Quantity-to-Date |
Disposal / Dumping Grounds |
Inert C&D materials disposed, m3 |
NIL |
276075.1 |
TKO137/ TM 38 |
Inert C&D materials recycled, m3 |
NIL |
18161 |
N/A |
Non-inert C&D materials disposed, m3 |
NIL |
1515.103 |
SENT Landfill |
Non-inert C&D materials recycled, m3 |
N/A |
N/A |
N/A |
Chemical waste disposed, kg |
NIL |
13860 |
SENT Landfill |
Marine Sediment (Type 1 – Open Sea
Disposal), m3 |
NIL |
240222 (Bulk volume) |
South of Cheung Chau |
Marine Sediment (Type 1 – Open Sea Disposal
(Dedicate Sites) & Type 2 – Confined Marine Disposal), m3 * |
NIL |
146445 (Bulk volume) |
East of Sha Chau |
4.5.4. There was no Marine Sediment (Type 1 –
Open Sea Disposal) and no Marine
Sediment (Type 1- Open Sea Disposal (Dedicate Sites) & Type 2- Confined
Marine Disposal) disposed of in this reporting quarter.
Contract no. HY/2009/15 -
Central-Wanchai Bypass – Tunnel (Causeway Bay Typhoon Shelter Section)
4.5.5. There was Inert C&D waste disposed in this
reporting period. No non-inert C&D waste was disposed in this reporting
period. Details of the waste flow table are summarized in Table 4.20.
Table 4.20 Details of Waste Disposal for Contract no. HY/2009/15
Waste Type |
Quantity this quarter |
Cumulative Quantity-to-Date |
Disposal / Dumping Grounds |
Remarks |
Inert C&D materials disposed, m3 |
NIL |
141579.2 |
Tuen Mun Area 38 |
NIL |
NIL |
65216 |
TKO137 FB |
NIL |
|
Inert C&D materials recycled, m3 |
8127.21 |
8127.21 |
HY/2010/08 |
NIL |
NIL |
304 |
Ex-PCWA |
NIL |
|
NIL |
111.9 |
TS4 |
NIL |
|
Non-inert C&D materials disposed, m3 |
NIL |
252.2 |
SENT Landfill |
NIL |
Non-inert C&D materials recycled, kg |
NIL |
299361.5 |
N/A |
NIL |
Chemical waste disposed, kg |
NIL |
8,200 |
N/A |
NIL |
Marine Sediment (Type 1 – Open Sea Disposal)
, m3 |
NIL |
156909 (Bulk Volume) |
South of Cheung Chau |
Dredging from TCBR1E /
TCBR1W / TCBR2/ TCBR3 / TCBR4 / Maintenance dredging |
Marine Sediment (Type 1 – Open Sea Disposal
(Dedicate Sites) & Type 2 – Confined Marine Disposal) , m3 |
3000 |
325796 (Bulk Volume) |
East of Sha Chau |
Dredging from TCBR1E /
TCBR1W / TCBR2/ TCBR3 / TCBR4 / Maintenance dredging |
Marine Sediment (Type 3 – Special Treatment
/ Disposal contained in Geosynthetic Containers) |
NIL |
12640 (Bulk Volume) |
East of Sha Chau |
Dredging from TCBR1W /
Maintenance dredging |
Marine Sediment (Type 2 – Confined Marine
Disposal), m3 |
NIL (Bulk Volume) |
9350 (Bulk Volume) |
East of Sha Chau |
Dredging from Eastern
Breakwater of CBTS |
Marine Sediment (Type 1 – Open Sea Disposal)
, m3 |
NIL (Bulk Volume) |
600 (Bulk Volume) |
East Sha Chau / South
of The Brothers |
Dredging from Phase 3
Mooring Re-arrangement |
Marine Sediment (Type 2– Confined Marine Disposal)
, m3 |
NIL (Bulk Volume) |
14,780 (Bulk Volume) |
South of The Brothers |
Dredging from Phase 3
Mooring Re-arrangement |
Marine Sediment (Type 3
– Special Treatment / Disposal contained in Geosynehetic Containers)
, m3 |
NIL (Bulk Volume) |
2,760 (Bulk Volume) |
South of The Brothers |
Dredging from Phase 3
Mooring Re-arrangement |
4.5.6. There was no Marine Sediment (Type 1 – Open Sea
Disposal) disposed in this reporting quarter. Marine Sediment (Type 1 – Open
Sea Disposal (Dedicate Sties) & Type 2 – Confined Marine Disposal) was disposed
in this reporting quarter.
Contract
no. HY/2009/19 – Central- WanChai Bypass Tunnel (North Point Section) and
Island Eastern Corridor Link
4.5.7. No Inert and non-inert C&D waste were disposed
of in this reporting quarter. Details of the waste flow table are summarized in
Table 4.21.
Table
4.21 Details of Waste Disposal for Contract no. HY/2009/19
Waste Type |
Quantity this month |
Cumulative
Quantity-to-Date |
Disposal / Dumping Grounds |
Inert C&D materials disposed, m3 |
NIL |
355921.04 |
TM38 |
Inert C&D materials
recycled, m3 |
NIL |
59367 |
N/A |
Non-inert C&D materials disposed, m3 |
NIL |
1068.6 |
N/A |
Non-inert C&D materials recycled, kg |
NIL |
333.14 |
N/A |
Chemical waste disposed, L |
NIL |
2.12 |
N/A |
Marine Sediment (Type 1 – Open Sea Disposal), m3 |
NIL |
162 |
South Cheung Chau |
Marine Sediment (Type 2 – Confined Marine Disposal) , m3 |
NIL |
681 |
East Sha Chau |
Marine Sediment (Type 1 – Open Sea Disposal (Dedicate Sites) &
Type 2 – Confined Marine Disposal) , m3 |
NIL |
4976.00 |
N/A |
4.5.8. There were no marine sediments Type1- Open Sea
Disposal and there were no Type 1 – Open Sea Disposal (Dedicate Sites) &
Type 2 – Confined Marine Disposal in this reporting quarter.
Contract
no. HK/2012/08 –Wan Chai Development Phase II – Central- Wan Chai Bypass at Wan
Chai West
4.5.9. No Inert and non-inert C&D waste was disposed
of in this reporting quarter. Details of the waste flow table are summarized in
Table 4.22.
Table
4.22 Details of Waste Disposal for Contract no. HK/2012/08
Waste Type |
Quantity this month |
Cumulative Quantity-to-Date |
Disposal / Dumping Grounds |
Inert C&D materials disposed, m3 |
NIL |
4131 |
TM38 |
Inert C&D materials recycled, m3 |
NIL |
NIL |
N/A |
Non-inert C&D materials disposed, m3 * |
NIL |
315 |
N/A |
Non-inert C&D materials recycled, kg |
NIL |
NIL |
N/A |
Chemical waste disposed, L |
NIL |
NIL |
N/A |
Marine Sediment (Type 1 – Open Sea Disposal),
m3 * |
NIL (Bulk volume) |
31759 (Bulk volume) |
South of Cheung Chau |
Marine Sediment (Type 1 – Open Sea Disposal (Dedicate Sites) &
Type 2 – Confined Marine Disposal) , m3 * |
NIL (Bulk volume) |
108542 (Bulk volume) |
South of The Brothers (from 27 Aug 2013 onwards) |
4.5.10. No Marine Sediment (Type 1 – Open Sea Disposal) disposed
in this reporting quarter. No marine sediment Type 1 – Open Sea Disposal
(Dedicate Sites) & Type 2 – Confined Marine Disposal generated disposed in
this reporting quarter.
Contract
no. HY/2010/08 –Central - Wan Chai Bypass (CWB) –Tunnel (Slip Road 8)
4.5.11. There was Inert C&D waste disposed in this
reporting period. No non-inert C&D waste was disposed in this reporting period.
Details of the waste flow table are summarized in Table 4.23
Table 4.23 Details of Waste Disposal for Contract no. HY/2010/08
Waste Type |
Quantity this month |
Cumulative Quantity-to-Date |
Disposal / Dumping Grounds |
Inert C&D materials disposed, m3 |
8320.5 7560.2 |
26849.2 19739.4 |
TM38 TKO137 |
Inert C&D materials recycled, m3 |
NIL |
NIL |
N/A |
Non-inert C&D materials disposed, m3 |
NIL |
NIL |
N/A |
Non-inert C&D materials recycled, kg |
NIL |
NIL |
N/A |
Chemical waste disposed, L |
NIL |
NIL |
N/A |
Marine Sediment (Type 1 – Open Sea Disposal) |
NIL |
55290 |
South Cheung Chau |
Marine Sediment (Type 1 – Open Sea Disposal (Dedicate Sites) & Type
2 – Confined Marine disposal) |
NIL |
27760 |
Brothers Island |
Marine Sediment (Type 3 – Special Treatment) |
NIL |
7780 |
Brothers Island |
Remarks: Contractor has clarified and
updated the cumulative quantity of the Inert C&D materials disposed in this
reporting quarter. Contractor has clarified and updated that no marine sediment
disposal recorded in this reporting quarter.
4.5.12. There was no Marine Sediment (Type 1 – Open Sea
Disposal), Marine Sediment (Type 3 – Special Treatment) and marine sediment Type
1 – Open Sea Disposal (Dedicate Sites) & Type 2 – Confined Marine Disposal disposed
in this reporting quarter.
5.0.1. The Event Action Plan for construction noise, air
quality and water quality are presented in Appendix 5.1.
5.1.1 Three limit level
exceedances were recorded at noise monitoring station M1a – Harbour Road Sports
Centre on 7, 13 and 21 June 2016 in June reporting month. The exceedances were
concluded as non-project related.
5.1.2 Three limit level
exceedances were recorded at noise monitoring station M6 – HK Baptist Church
Henrietta Secondary School on 7, 13 and 21 June 2016 in June reporting month.
The exceedances were concluded as non-project related.
5.1.3 One limit level
exceedance was recorded at noise monitoring station M1a – Habour Road Sports
Center on 28 June 2016 in July reporting month. The exceedance was concluded as
non-project related.
5.1.4 One limit level
exceedance was recorded at noise monitoring station M6 – HK Baptist Church
Henrietta Secondary School on 12 July 2016 in July reporting month. The
exceedance was concluded as non-project related.
5.1.5 No action or limit
level exceedance was recorded in August reporting month.
5.1.6 Noise monitoring results measured in this reporting
period are reviewed and summarized.
Details of graphical presentation can be referred in Appendix 4.1.
5.2.1 No action or limit level exceedance for TSP monitoring was recorded
in June reporting month.
5.2.2 No action or limit level exceedance for TSP monitoring was recorded
in July reporting month.
5.2.3 One 1hr TSP action level exceedance was recorded at CMA1b – Oil
Street Site Office on 27 August 2016 in August reporting month.
5.2.4 The odour patrol along the odour route with 7 sniffing locations
was conducted by a qualified odour patrol member on 5 July 2016 and 20 July
2016 at the concerned hours (afternoon for higher daily temperature). No action
and limit level was recorded during July reporting month.
5.2.5 The odour patrol along the odour route with 7 sniffing locations
was conducted by a qualified odour patrol member on 1 August 2016 and 17 August
2016 at the concerned hours (afternoon for higher daily temperature). No action
and limit level was recorded during August reporting month..
5.3.1 There were 1 limit level of turbidity
exceedances and 2 action level of suspended solid exceedances recorded in June
reporting month. Investigation found that the turbidity exceedances and
suspended solid exceedances recorded in June reporting month were not related
to Project works.
5.3.2 There were 1 action and 1 limit level of
turbidity exceedances recorded in July reporting month. Investigation found
that the turbidity exceedances recorded in July reporting month were not
related to Project works.
5.3.3 There were 2 action and 1 limit level of
turbidity exceedances recorded in August reporting month. Investigation found
that the turbidity exceedances recorded in August reporting month were not
related to Project works.
5.3.4 There was 1 action level and 4 limit
level exceedances recorded for enhanced dissolved oxygen monitoring in June
reporting month. Investigation found that the exceedance was not related to
Project works.
5.3.5 There was 1 action level and 2 limit
level exceedances recorded for enhanced dissolved oxygen monitoring in this
July month. Investigation found that the exceedance was not related to Project
works.
5.3.6 There was 1 action level and 12 limit
level exceedances recorded for enhanced dissolved oxygen monitoring in August
reporting month. Investigation found that the exceedance was not related to
Project works.
5.5.1. There was no non-compliance from the site audits in
the reporting period. During environmental site inspections conducted during
the reporting period, minor deficiencies were noted.
5.5.1
There was no non-compliance from the site
audits in the reporting quarter.
5.6.1
There was no particular action taken since no
project-related non-compliance was recorded from the site audits in this
reporting quarter.
6.0.1. No environmental complaint was received
in June reporting month.
6.0.2. There was one environmental complaint
received in July reporting month.
6.0.3. A public complaint referred by EPD was
received by ET on 06 July 2016 (Case Ref:. H05/RS/00016226-16). The complainant
reported that a derrick barge in green colour under Contract HY/2009/15 moored
near Royal Hong Kong Yacht Club emitted dark smoke since mid of June 2016.
6.0.4. ET confirmed with the Resident Site
Staff that the concerned green derrick barge was identified as Yue Fat 206
(YF206) and the concerned green derrick barge was operated within the Ex-PCWA
area for excavation works intermittently across the period from15 June 2016 to
30 June 2016. The concerned green derrick barge YF206 within Ex-PCWA area was
no longer deployed under Contract HY/2009/15 after 02 July 2016.
6.0.5. Follow-up inspection was conducted on 11
July 2016, the concerned derrick barge YF206 was not deployed at the concerned
location and no dark smoke was observed from other derrick barge operating
on-site. Nevertheless, in view of the public concern, the Contractor of
HY/2009/15 was reminded to conduct regular checking and maintenance for all
derrick barges deployed on site to ensure only well maintained equipment is
used to avoid potential dark smoke emission affecting nearby surroundings.
6.0.6. There was one environmental complaint
received in August reporting month.
6.0.7. A public complaint referred by EPD was
received on 25 August 2016 (Case Ref.: H08/RS/00012592-16). The complainant
reported that muddy water was observed at Causeway Bay Typhoon Shelter.
6.0.8. ET confirmed with the Resident Site
Staff that no marine construction activities were undertaken at the concerned
location at East of Temporary Reclamation Zone TS3 within Causeway Bay Typhoon
Shelther from 14:00hrs to 17:00hrs on 25 May 2016. Site control measures
including the following were implemented by the Contractor of HY/2010/08 around
the concerned location. Site control measures including i) Wastewater treatment
facilities (AquaSed) were installed at TS3 for treatment of wastewater
generated during construction activities. Sampling of effluent from AquaSed was
conducted by the Contractor of HY/2010/08 and all results complied with the
requirements in the Discharge Licence. Visual inspection and pH measurement of
effluent were conducted daily by Environmental Supervisors and all results
passed. ii) Brick/ earth/ sandbag bunds were installed alongside the site
perimeter of TS3 to prevent muddy runoff into the sea. iii) Piping with idled
ends were removed to prevent accidental discharge of untreated wastewater. iv)
Diver inspection for silt curtains and/ or impermeable barriers was conducted
on an ad-hoc basis. vii) Temporary cut slopes were shotcreted or properly
covered with tarpaulin sheets. viii) Regular inspections were conducted by the
RSS and Contractor’s environmental representatives on regular basis on the
conditions of mitigation measures implemented on site.
6.0.9. Based on the complainant photo
information, the exposed soil slope at Temporary Reclamation Zone TS3 were
observed protected by covering and enclosed by double layer of impermeable
barrier/ silt curtain and no contaminated discharge was identified. In
addition, based on information from Hong Kong Observatory, the tidal condition
on 25 May 2016 afternoon was found to be ebb-tide while non construction works
marine vessel movements around the identified muddy plume within Causeway Bay
Typhoon Shelter was observed in the complainant photo information.
6.0.10. Based on review on relevant records, no
contaminated surface runoff and no contaminated discharge was identified at the
concerned location during the environmental site inspection conducted on 25 May
2016. Follow up inspection was conducted on 31 August 2016 and seawall
construction and filing works at the Temporary Reclamation Zone TS3 was
observed completed. No contaminated discharge and no contaminated surface
runoff was found.
6.0.11. Nevertheless, the contractor of
HY/2010/08 was reminded to maintain appropriate bunding at seawall boundary for
protection against potential surface runoff related impact. Also, the
Contractor of HY/2010/08 was reminded to maintain proper site drainage for
effluent collection and treatment system to ensure the compliance with relevant
discharge license..
6.0.12.
The details of cumulative complaint
log and summary of complaints are presented in Appendix
6.1.
6.0.13. Cumulative statistic on complaints and successful prosecutions
are summarized in Table 6.1 and Table 6.2 respectively.
Table 6.1 Cumulative Statistics on Complaints
Reporting Period |
No. of Complaints |
Commencement works
(Mar 2010) to last reporting quarter |
45 |
June 2016 – August 2016 |
2 |
Project-to-Date |
47 |
Table 6.2 Cumulative Statistics on Successful
Prosecutions
Environmental Parameters |
Cumulative No. Brought Forward |
No. of Successful Prosecutions this quarter (Offence Date) |
Cumulative No. Project-to-Date |
Air |
- |
0 |
0 |
Noise |
- |
0 |
0 |
Water |
- |
0 |
0 |
Waste |
- |
0 |
0 |
Total |
- |
0 |
0 |
7.0.1. According
to Condition 3.4 of the EP-356/2009, this section addresses the relevant
cumulative construction impact due to the concurrent activities of the current
projects including the Central Reclamation Phase III, Central-Wanchai Bypass
and Island Eastern Corridor Link projects.
7.0.2. According
to the Final EM&A Report of Central Reclamation Phase III (CRIII) for
Contract HK 12/02, the major construction activities were completed by end of
January 2014 and no construction activities were undertaken thereafter and the
water quality monitoring was completed in October 2011 and no Project-related exceedance
was recorded for air and noise monitoring.
It can be concluded that cumulative construction impact due to the
concurrent activities of the current projects with the Central Reclamation
Phase III (CRIII) was insignificant.
7.0.3. According to the construction programme
of Central-Wanchai Bypass at Wanchai West at the Central Reclamation Phase III
area include structural works for tunnel construction, road works and drainage
works, and seawall modification were performed in August 2016 reporting month. As no project related exceedance were
recorded during the reporting period, cumulative construction impact due to the
concurrent activities of the current projects with the Central Reclamation
Phase III (CRIII) was considered as insignificant.
7.0.4.
According
to the construction programme of Wan Chai Development Phase II, Central-Wan
Chai Bypass and Island Eastern Corridor Link projects, the major construction
activities under Wan Chai Development Phase II were tunnel works at Wan Chai
East and back filling works, culvert reinstatement and road and drain works at
Wan Chai West. The major construction activities under Central-Wan Chai Bypass
and Island Eastern Corridor Link Projects were road works and ventilation
building construction at Central Interchange, temporary reclamation removal
works at Ex-PCWAW, ELS works and retaining wall construction at Victoria Park,
ELS works and tunnel works at TS3; bridge construction, piling and tunnel works
at North Point area in the reporting month. In addition, other non-Wan Chai
Development Phase II, Central-Wan Chai Bypass and Island Eastern Corridor Link
projects was observed undertaken at Wan Chai
North and North Point area.
7.0.5. No significant air impact from
construction activities was anticipated in the reporting month. Besides, no
project related exceedance was recorded during the air and noise environmental
monitoring events in the reporting month. Thus, it is evaluated that the
cumulative construction impact from the concurrent projects including Central
Reclamation Phase III (CRIII), Wan Chai Development Phase II (WDII),
Central-WanChai Bypass (CWB), Island Eastern Corridor Link projects (IECL) was
insignificant.
8.0.1. The EM&A programme was carried out in
accordance with the EM&A Manual requirements, minor alterations to the
programme proposed were made in response to changing circumstances.
8.0.2. No non-compliance was noted and no prosecution was
received in this reporting quarter.
8.0.3. The construction programmes
of individual contracts are provided in Appendix 8.1.