Executive
Summary
1.1 Background
1.2 Scope of Report
1.3 Organization Structure
1.4 Summary of Construction Works
2.1 Air Quality
2.2 Noise Monitoring
2.3 Water Quality Monitoring
2.4 Dolphin Monitoring
2.5 EM&A Site Inspection
2.6 Waste Management Status
2.7 Environmental Licenses and Permits
2.8 Implementation Status of Environmental Mitigation
Measures
2.9 Summary of Exceedances of the Environmental Quality
Performance Limit
2.10 Summary of Complaints, Notification of Summons and
Successful Prosecutions
3.1 Construction Programme for the Coming Month
3.2 Key Issues for the Coming Month
3.3 Monitoring Schedule for the Coming Month
4 Conclusions and Recommendations
4.1 Conclusions
List
of Appendices
Appendix
A Project Organization for Environmental Works
Appendix
B Three Month Rolling Construction Programmes
Appendix
C Implementation Schedule of Environmental Mitigation
Measures (EMIS)
Appendix
D Summary of Action and Limit Levels
Appendix
E Calibration Certificates of Monitoring Equipment
Appendix
F EM&A Monitoring Schedules
Appendix
G Impact Air Quality Monitoring Results and Graphical
Presentation
Appendix
H Meteorological Data for the Reporting Month
Appendix
I Impact Noise Monitoring Results and Graphical
Presentation
Appendix
J Impact Water Quality Monitoring Results and Graphical
Presentation
Appendix
K Impact Dolphin Monitoring Survey Results
Appendix
L Event Action Plan
Appendix
M Monthly Summary of Waste Flow Table
Under Contract
No. HY/2012/07, Gammon Construction Limited (GCL) is commissioned by the Highways
Department (HyD) to undertake the design and construction of the Southern
Connection Viaduct Section of the Tuen Mun – Chek Lap Kok Link Project (TM-CLK
Link Project) while AECOM Asia Company Limited was appointed by HyD as the
Supervising Officer. For implementation
of the environmental monitoring and audit (EM&A) programme under the
Contract, ERM-Hong Kong, Limited (ERM) has been appointed as the Environmental
Team (ET). Ramboll Hong Kong Ltd. was
employed by the HyD as the Independent Environmental Checker (IEC) and
Environmental Project Office (ENPO) in accordance with Environmental Permit No. EP-354/2009/A. Further
applications for variation of environmental permit (VEP), EP-354/2009/B, EP-354/2009/C
and EP-354/2009/D, were granted on 28
January 2014, 10 December 2014 and 13 March 2015, respectively.
The southern landfall of TM-CLK Link lies alongside
the Hong Kong - Zhuhai - Macao Bridge Hong Kong Boundary Crossing Facilities
(HKBCF) where a reclamation area is constructed by Contract No. HY/2010/02 under Environmental
Permit No. EP-353/2009/K and
EP-354/2009/D. Upon the agreement
and confirmation between the Supervising Officer Representatives and
Contractors of HY/2010/02 and HY/2012/07 in September 2015, part of
the reclamation area for southern landfall under EP-353/2009/K and
EP-354/2009/D was handed-over to Contract
No. HY/2012/07. Another part of the
southern landfall area under EP-354/2009/D
was handed-over to Contract No.
HY/2012/07 after completion of reclamation works by Contract No. HY/2010/02 in June 2016.
The construction phase of the Contract commenced on 31
October 2013 and will be tentatively completed by 2018. The impact monitoring of the EM&A
programme, including air quality, noise, water quality and marine ecological
monitoring as well as environmental site inspections, commenced on 31 October
2013.
This is the Fifty-fifth Monthly EM&A report
presenting the EM&A works carried out during the period from 1 to 31 May
2018 for the Southern Connection Viaduct
Section in accordance with the Updated EM&A Manual of the TM-CLK
Link Project. As informed by the
Contractor, major activities in the reporting period included:
Land-based Works
· Pier
construction;
· Re-alignment
of Cheung Tung Road;
· Road
works along North Lantau Highway;
· Installation
of pier head and deck segments;
· Asphalt
paving;
· Construction
of sign gantries, light poles and street furniture;
· Parapets
and barriers installation; and
· Slope
work of Viaducts A, B, C & D.
A summary of monitoring and audit activities conducted
in the reporting period is listed below:
24-hour TSP Monitoring 6
sessions
1-hour TSP Monitoring 6
sessions
Water Quality Monitoring 13 sessions
Noise Monitoring 6
sessions
Impact Dolphin Monitoring 2 sessions
Joint Environmental Site Inspection 5 sessions
Breaches of
Action and Limit Levels for Air Quality
No exceedance of Action and Limit Levels was recorded
for construction air quality monitoring in the reporting month.
Breaches of
Action and Limit Levels for Noise
No exceedance of Action and Limit Levels was recorded
for construction noise monitoring in the reporting month.
Breaches of
Action and Limit Levels for Water Quality
One (1) Action Level of Dissolved Oxygen (DO)
exceedance was recorded for water quality impact monitoring in the reporting
month.
Impact Dolphin
Monitoring
One
(1) Limit Level exceedance was observed for the quarterly dolphin monitoring
data between March and May 2018, whilst no unacceptable
impact from the construction activities of the TM-CLKL Southern Connection
Viaduct Section on Indo-Pacific humpback dolphin Sousa chinensis (i.e. Chinese White Dolphin) was noticeable from
general observations. Due to monthly
variation in dolphin occurrence within the Study Area, it would be more
appropriate to draw conclusion on whether any impacts on dolphins have been
detected related to the construction activities of the TM-CLKL Southern
Connection Viaduct Section in the quarterly EM&A reports, in which
comparison on distribution, group size and encounter rates of dolphins between
the quarterly impact monitoring period and baseline monitoring period will be
made.
Daily marine mammal exclusion zone monitoring was
undertaken during the period of marine works under this Contract. No sighting of the Chinese White Dolphin was
recorded in May 2018 during the exclusion zone monitoring.
Environmental
Complaints, Non-compliance & Summons
There was no environmental complaint, notification of
summons or successful prosecution recorded in the reporting period.
Summary of
Marine Travel Route record
Summary
of marine travel route record for April and this reporting period will be
provided when available.
Reporting Change
There was no reporting change in the reporting period.
Upcoming Works for the Next Reporting Period
Works to be undertaken in the next monitoring period
of June 2018 include the following:
Land-based Works
· Pier
construction;
· Re-alignment
of Cheung Tung Road;
· Road
works along North Lantau Highway;
· Installation
of pier head and deck segments;
· Asphalt
paving;
· Construction
of sign gantries, light poles and street furniture;
· Parapets
and barriers installation; and
· Slope
work of Viaducts A, B, C & D.
Future Key
Issues
Potential environmental impacts arising from the above
upcoming construction activities in the next reporting month of June 2018 are
mainly associated with dust, noise, marine water quality, marine ecology and
waste management issues.
According to the findings of the Northwest New
Territories (NWNT) Traffic and Infrastructure Review conducted by the Transport
Department, Tuen Mun Road, Ting Kau Bridge, Lantau Link and North Lantau
Highway would be operating beyond capacity after 2016. This forecast has been based on the estimated
increase in cross boundary traffic, developments in the Northwest New
Territories (NWNT), and possible developments in North Lantau, including the
Airport developments, the Lantau Logistics Park (LLP) and the Hong Kong –
Zhuhai – Macao Bridge (HZMB). In order
to cope with the anticipated traffic demand, two new road sections between NWNT
and North Lantau – Tuen Mun – Chek Lap Kok Link (TM-CLKL) and Tuen Mun Western
Bypass (TMWB) are proposed.
An Environmental Impact Assessment (EIA) of TM-CLKL
(the Project) was prepared in accordance with the EIA Study Brief (No.
ESB-175/2007) and the Technical
Memorandum of the Environmental Impact Assessment Process (EIAO-TM). The EIA Report was submitted under the
Environmental Impact Assessment Ordinance (EIAO) in August 2009. Subsequent to the approval of the EIA Report
(EIAO Register Number AEIAR-146/2009), an Environmental Permit (EP-354/2009) for TM-CLKL was granted by
the Director of Environmental Protection (DEP) on 4 November 2009, and EP
variation (EP-354/2009/A) was issued
on 8 December 2010.
Under Contract
No. HY/2012/07, Gammon Construction Limited (GCL) is commissioned by the
Highways Department (HyD) to undertake the design and construction of the
Southern Connection Viaduct Section of TM-CLKL (“the Contract”) while AECOM
Asia Company Limited was appointed by HyD as the Supervising Officer. For implementation of the environmental
monitoring and audit (EM&A) programme under the Contract, ERM-Hong Kong,
Limited (ERM) has been appointed as the Environmental Team (ET). Ramboll Hong Kong Ltd. was employed by HyD as
the Independent Environmental Checker (IEC) and Environmental Project Office
(ENPO) in accordance with Environmental
Permit No. EP-354/2009/A. Further applications for variation of
environmental permit (VEP), EP-354/2009/B,
EP-354/2009/C and EP-354/2009/D, were granted on 28
January 2014, 10 December 2014 and 13 March 2015, respectively.
The southern landfall of TM-CLK Link lies alongside
the Hong Kong - Zhuhai - Macao Bridge Hong Kong Boundary Crossing Facilities
(HKBCF) where a reclamation area is constructed by Contract No. HY/2010/02 under Environmental
Permit No. EP-353/2009/K and
EP-354/2009/D. Upon the agreement
and confirmation between the Supervising Officer Representatives and
Contractors of HY/2010/02 and HY/2012/07 in September 2015, part of
the reclamation area for southern landfall under EP-353/2009/K and
EP-354/2009/D was handed-over to Contract
No. HY/2012/07. Another part of the
southern landfall area under EP-354/2009/D
was handed-over to Contract No.
HY/2012/07 after completion of reclamation works by Contract No. HY/2010/02 in June 2016.
The construction phase of the Contract commenced on 31
October 2013 and will be tentatively completed by 2018. The impact monitoring phase of the EM&A
programme, including air quality, noise, water quality and marine ecological
monitoring as well environmental site inspections, commenced on 31 October
2013.
The general layout plan of the Contract components is
presented in Figures 1.1 & 1.2a to l.
This is the Fifty-fifth Monthly EM&A Report under
the Contract No. HY/2012/07 Tuen Mun –
Chek Lap Kok Link – Southern Connection Viaduct Section. This report presents a summary of the
environmental monitoring and audit works in May 2018.
The organization structure of the Contract is shown in
Appendix A. The
key personnel contact names and contact details are summarized in Table 1.1 below.
Table 1.1 Contact Information of Key Personnel
Party |
Position |
Name |
Telephone |
Fax |
HyD (Highways
Department) |
Project
Coordinator |
Stanley Chan |
2762 3406 |
3188 6614 |
|
Senior
Engineer |
Steven Shum |
2762 4133 |
3188 6614 |
SOR (AECOM Asia
Company Limited) |
Chief Resident
Engineer |
Daniel Ip |
3553 3800 |
2492 2057 |
|
Resident
Engineer |
Kingman Chan |
3691 3950 |
3691 2899 |
ENPO / IEC (Ramboll Hong Kong Ltd.) |
ENPO Leader |
Y.H. Hui |
3465
2850 |
3465 2899 |
IEC |
Dr. F.C. Tsang |
3465
2851 |
3465 2899 |
|
Contractor (Gammon
Construction Limited) |
Environmental
Manager |
Brian Kam |
3520 0387 |
3520 0486 |
Environmental
Officer |
Roy Leung |
3520 0387 |
3520 0486 |
|
|
24-hour
Complaint Hotline |
|
9738 4332 |
|
ET (ERM-HK) |
ET Leader |
Jovy Tam |
2271 3113 |
2723 5660 |
The construction phase of the Contract commenced on 31
October 2013. The three-month rolling
construction programme is shown in Appendix B.
As informed by the Contractor, details of the major
works carried out in this reporting month are listed below:
Land-based Works
· Pier
construction;
· Re-alignment
of Cheung Tung Road;
· Road
works along North Lantau Highway;
· Installation
of pier head and deck segments;
· Asphalt
paving;
· Construction
of sign gantries, light poles and street furniture;
· Parapets
and barriers installation; and
· Slope
work of Viaducts A, B, C & D.
The
locations of the construction activities are shown in Figure 1.3.
The Environmental Sensitive Receivers in the vicinity of the Project are
shown in Figure 1.4.
The environmental mitigation measures implementation
schedule is presented in Appendix C.
The EM&A programme required environmental
monitoring for air quality, noise, water quality and marine ecology as well as
environmental site inspections for air quality, noise, water quality, waste
management, marine ecology and landscape and visual impacts. The EM&A requirements and related
findings for each component are summarized in the following sections.
In accordance with the Updated EM&A Manual, impact
1-hour TSP monitoring was conducted three (3) times every six (6) days and
impact 24-hour TSP monitoring was carried out once every six (6) days when the
highest dust impact was expected. The
Action and Limit Levels of the air quality monitoring is provided in Appendix D.
Table 2.1 Locations of Impact Air Quality Monitoring Stations
Monitoring Station |
Location |
Description |
Monitoring Dates |
ASR 9 |
MTR Depot |
On the ground
nearby MTR Depot Entrance |
4, 10, 16, 19,
25 and 31 May 2018 |
ASR 8A |
Area 4 |
On ground at
the works area, Area 4 |
4, 10, 16, 19,
25 and 31 May 2018 |
High Volume Samplers (HVSs)
were used for 1-hour TSP and 24-hour TSP monitoring at ASR8A and ASR9 in accordance with the requirements of the Updated
EM&A Manual. The TSP monitoring
stations are illustrated in Figure 2.1 and detailed
in Table 2.1. Wind meter was deployed at Area 4 for logging
wind speed and wind direction. Copies
of the calibration certificates for the equipment are presented in Appendix E. Details of the deployed equipment are given
in Table 2.2.
Table 2.2 Air Quality Monitoring Equipment
Equipment |
Brand and Model |
High
Volume Sampler |
Tisch
Environmental Mass Flow Controlled Total Suspended Particulate
(TSP) High Volume Sampler (Model No. TE-5170) |
Wind
Sensor |
Global
Water (Wind Speed Sensor: WE550; Wind Direction Sensor: WE570) |
Wind
Anemometer for calibration |
Lutron
(Model No. AM-4201) |
The schedule for air quality monitoring in May 2018 is
provided in Appendix F.
The monitoring results for 1-hour TSP and 24-hour TSP
are summarized in Tables 2.3 and 2.4 respectively. Detailed impact air quality monitoring
results are presented in Appendix G.
Table 2.3 Summary of 1-hour TSP Monitoring Results in the Reporting
Period
Monitoring Station |
Average (µg/m3) |
Range (µg/m3) |
Action Level (µg/m3) |
Limit Level (µg/m3) |
ASR
8A |
86 |
14-236 |
394 |
500 |
ASR
9 |
86 |
14-200 |
393 |
500 |
Table 2.4 Summary of 24-hour TSP Monitoring Results in the Reporting
Period
Monitoring Station |
Average (µg/m3) |
Range (µg/m3) |
Action Level (µg/m3) |
Limit Level (µg/m3) |
ASR
8A |
35 |
10-65 |
178 |
260 |
ASR
9 |
46 |
25-75 |
178 |
260 |
The major dust sources in the reporting period included
construction activities under the Contract as well as nearby traffic emissions.
All 1-hour and 24-hour TSP results were below
the Action and Limit Levels at all monitoring locations in the reporting
period. No action is thus required to be
undertaken in accordance with the Event Action Plan presented in Appendix L.
Meteorological information collected at ASR8A including wind speed and wind
direction is provided in Appendix H.
In accordance with the Updated EM&A Manual, impact
noise monitoring was conducted once per week during the construction phase of
the Contract. The Action and Limit Level
of the noise monitoring is provided in Appendix D.
Noise monitoring was performed on 4, 10, 16, 19, 25
and 31 May 2018 using sound level meter at the designated monitoring station
NSR1A (Figure 2.2; Table 2.5) in accordance with the
requirements stipulated in the Updated EM&A Manual. Acoustic calibrator was deployed to check the
sound level meters at a known sound pressure level. Details of the deployed equipment are
provided in Table 2.6. Copies of the calibration certificates for
the equipment are presented in Appendix E.
Table 2.5 Location of Impact Noise Monitoring Station
Monitoring Station |
Location |
Description |
Parameter |
Frequency and Duration |
Monitoring Dates |
NSR 1A |
Pak Mong
Village Pavilion |
On the ground at
the village entrance |
30-minute
measurement at each monitoring station between 0700 and 1900 on normal
weekdays (Monday to Saturday). Leq, L10 and L90 would
be recorded. |
At least once
per week |
4, 10, 16, 19,
25 and 31 May 2018 |
Table 2.6 Noise Monitoring Equipment
Equipment |
Brand and Model |
Integrated
Sound Level Meter |
Rion NL-31 |
Acoustic
Calibrator |
Rion NC-73 |
The schedule for construction noise monitoring in the
reporting period is provided in Appendix F.
Results for noise monitoring are summarized in Table 2.7 and the monitoring data is
provided in Appendix I.
Table 2.7 Summary of Construction Noise Monitoring Results in the
Reporting Period
|
Average , dB(A), Leq (30mins) |
Range, dB(A), Leq (30mins) |
Limit Level, dB(A), Leq (30mins) |
NSR
1A |
63 |
62-64 |
75 |
No noise Action or Limit Level exceedance was recorded
in the reporting month. No action is
thus required to be undertaken in accordance with the Event Action Plan
presented in Appendix L.
Major noise sources during the noise monitoring
included noise from crane and excavator operation, and nearby traffic noise and
aircraft noise.
Station ID |
Type |
Coordinates |
*Parameters,
unit |
Frequency |
Depth |
|
|
|
Easting |
Northing |
|
|
|
IS(Mf)9 |
Impact Station (Close to HKBCF construction site) |
813273 |
818850 |
Temperature(°C)
pH (pH unit)
Turbidity (NTU)
Water depth (m)
Salinity (ppt)
Dissolved Oxygen (DO)
(mg/L and % of saturation) · Suspended Solid (SS) (mg/L) |
Impact monitoring: 3 days per
week, at mid-flood and mid-ebb tides during the construction period of the
Contract |
3 water depths: 1m below sea surface, mid-depth and 1m above sea bed.
If the water depth is less than 3m, mid-depth sampling only. If water depth less than 6m, mid-depth may
be omitted |
IS(Mf)16 |
Impact
Station (Close to HKBCF construction site) |
814328 |
819497 |
|||
IS8 |
Impact
Station (Close to HKBCF construction site) |
814251 |
818412 |
|||
SR4(N) |
Sensitive
receiver (Tai Ho Inlet) |
814705 |
817859 |
|||
SR4a |
Sensitive
receiver |
815247 |
818067 |
|||
CS(Mf)3(N) |
Control Station |
808814 |
822355 |
|||
CS(Mf)5 |
Control
Station |
817990 |
821129 |
|||
*Notes: Water Quality Monitoring Station CS(Mf)3 was
relocated to CS(Mf)3(N) since 2 May 2017. Water Quality Monitoring Station SR4 was relocated
to SR4(N) since 2 March 2018. |
Table 2.9 Water Quality Monitoring Equipment
Equipment |
Brand and Model |
Multi-parameters (Dissolved Oxygen, Salinity, Turbidity,
Temperature, pH) |
YSI ProDSS / YSI 6920 / YSI 6920 V2 |
|
|
Positioning Equipment |
Furuno GP-170 |
Water Depth Detector |
Lowrance Mark 5x / Garmin Striker 4 |
Water Sampler |
WildCo Vertical Alpha Bottles 1120-2.2L /1120-3.2L Aquatic Research Instrument Vertical/Horizontal Point Water Sampler
2.2L / 3.0L |
One (1) Action Level of Dissolved
Oxygen (DO) exceedance was recorded for water quality impact monitoring in the
reporting month. No action is thus
required to be undertaken in accordance with the Event Action Plan as presented
in Appendix L.
Impact dolphin monitoring is required to be conducted
by a qualified dolphin specialist team to evaluate whether there have been any
effects on the Indo-Pacific humpback dolphin Sousa chinensis (i.e. Chinese White Dolphin) from the
Contract. In order to fulfil the
EM&A requirements and make good use of available resources, the on-going
impact line transect dolphin monitoring data collected by HyD’s Contract No. HY/2011/03 Hong
Kong-Zhuhai-Macao Bridge. Hong Kong Link Road - Section between Scenic Hill and
Hong Kong Boundary Crossing Facilities on the monthly basis is adopted to
avoid duplicates of survey effort.
Table 2.10
summarizes the equipment used for the impact dolphin monitoring.
Table 2.10 Dolphin Monitoring Equipment
Equipment |
Model |
|
Global Positioning
System (GPS) Camera Laser Binoculars Marine Binocular Vessel for
Monitoring |
Garmin 18X-PC Geo One Phottix Nikon D90 300m 2.8D fixed focus Nikon D90 20-300m zoom lens Infinitor LRF 1000 Bushell 7 x 50 marine binocular with compass and reticules 65 foot single engine motor vessel with viewing platform 4.5m above
water level |
|
Dolphin
monitoring should cover all transect lines in Northeast Lantau
(NEL) and the Northwest Lantau (NWL) survey areas twice per month throughout the entire
construction period. The monitoring data
should be compatible with, and should be made available for, long-term studies
of small cetacean ecology in Hong Kong.
In order to provide a suitable long-term dataset for comparison,
identical methodology and line transects employed in baseline dolphin monitoring
was followed in the impact dolphin monitoring.
The
impact dolphin monitoring was carried out in the NEL and NWL along the line
transect as depicted in Figure 2.4. The co-ordinates of all transect lines are
shown in Table 2.11
below ([1]).
Table
2.11 Impact Dolphin Monitoring Line Transect
Co-ordinates
Line No. |
Easting |
Northing |
Line No. |
Easting |
Northing |
||
1 |
Start Point |
804671 |
815456 |
13 |
Start Point |
816506 |
819480 |
1 |
End Point |
804671 |
831404 |
13 |
End Point |
816506 |
824859 |
2 |
Start Point |
805476 |
820800 |
14 |
Start Point |
817537 |
820220 |
2 |
End Point |
805476 |
826654 |
14 |
End Point |
817537 |
824613 |
3 |
Start Point |
806464 |
821150 |
15 |
Start Point |
818568 |
820735 |
3 |
End Point |
806464 |
822911 |
15 |
End Point |
818568 |
824433 |
4 |
Start Point |
807518 |
821500 |
16 |
Start Point |
819532 |
821420 |
4 |
End Point |
807518 |
829230 |
16 |
End Point |
819532 |
824209 |
5 |
Start Point |
808504 |
821850 |
17 |
Start Point |
820451 |
822125 |
5 |
End Point |
808504 |
828602 |
17 |
End Point |
820451 |
823671 |
6 |
Start Point |
809490 |
822150 |
18 |
Start Point |
821504 |
822371 |
6 |
End Point |
809490 |
825352 |
18 |
End Point |
821504 |
823761 |
7 |
Start Point |
810499 |
822000* |
19 |
Start Point |
822513 |
823268 |
7 |
End Point |
810499 |
824613 |
19 |
End Point |
822513 |
824321 |
8 |
Start Point |
811508 |
821123 |
20 |
Start Point |
823477 |
823402 |
8 |
End Point |
811508 |
824254 |
20 |
End Point |
823477 |
824613 |
9 |
Start Point |
812516 |
821303 |
21 |
Start Point |
805476 |
827081 |
9 |
End Point |
812516 |
824254 |
21 |
End Point |
805476 |
830562 |
10 |
Start Point |
813525 |
821176 |
22 |
Start Point |
806464 |
824033 |
10 |
End Point |
813525 |
824657 |
22 |
End Point |
806464 |
829598 |
11 |
Start Point |
814556 |
818853 |
23 |
Start Point |
814559 |
821739 |
11 |
End Point |
814556 |
820992 |
23 |
End Point |
814559 |
824768 |
12 |
Start Point |
815542 |
818807 |
24 |
Start Point |
805476 |
815900 |
12 |
End Point |
815542 |
824882 |
24 |
End Point |
805476 |
819100 |
The Action and Limit levels of dolphin impact
monitoring are shown in Appendix D. The Event and Action plan is presented in Appendix L.
Dolphin monitoring was carried out on 7, 10, 16 and 30
May 2018 (Appendix F).
A total of 261.40 km of survey effort was collected,
with 83.9% of the total survey effort being conducted under favourable weather
conditions (i.e. Beaufort Sea State 3 or below with good visibility) during the
surveys in May 2018. Among the two
areas, 95.70 km and 165.70 km of survey effort were collected from NEL and NWL
survey areas, respectively. The total
survey effort conducted on primary and secondary lines were 189.44 km and 71.96
km, respectively. The survey efforts are
summarized in Appendix K.
No Chinese White Dolphins were sighted during the two sets of monitoring surveys in
May 2018.
Encounter
rates of Chinese White Dolphins are deduced from the survey effort and
on-effort sighting data made under favourable conditions (Beaufort 3 or below)
in May 2018 are
shown in Tables 2.12 & 2.13.
Table 2.12 Individual Survey Event Encounter Rates
|
|
Encounter rate (STG) (no. of on-effort
dolphin sightings per 100 km of survey effort) |
Encounter rate (ANI) (no. of dolphins
from all on-effort sightings per 100 km of survey effort) |
Primary
Lines Only |
Primary
Lines Only |
||
NEL |
Set
1: May 7th / 10th |
0.0 |
0.0 |
Set
2: May 16th / 30th |
0.0 |
0.0 |
|
NWL |
Set
1: May 7th / 10th |
0.0 |
0.0 |
Set
2: May 16th / 30th |
0.0 |
0.0 |
|
Note: Dolphin Encounter Rates are deduced from
the two sets of surveys ( two surveys in each set) in May 2018 in Northeast (NEL) and
Northwest Lantau (NWL) |
Table 2.13 Monthly Average Encounter Rates
|
Encounter rate (STG) (no. of on-effort
dolphin sightings per 100 km of survey effort) |
Encounter rate (ANI) (no. of dolphins from all on-effort sightings per
100 km of survey effort) |
||
Primary
Lines Only |
Both Primary and Secondary Lines |
Primary
Lines Only |
Both Primary and Secondary Lines |
|
Northeast
Lantau |
0.0 |
0.0 |
0.0 |
0.0 |
Northwest
Lantau |
0.0 |
0.0 |
0.0 |
0.0 |
Note: Overall dolphin encounter rates (sightings
per 100 km of survey effort) from all four surveys are conducted in May 2018 on primary lines only
as well as both primary lines and secondary lines in Northeast and Northwest
Lantau
One (1) Limit Level exceedance was
observed for the quarterly dolphin monitoring data between March and May 2018,
whilst no unacceptable impact from the construction
activities of the TM-CLKL Southern Connection Viaduct Section on Indo-Pacific
humpback dolphin Sousa chinensis
(i.e. Chinese White Dolphin) was noticeable from general observations. Due to monthly variation in dolphin
occurrence within the Study Area, it would be more appropriate to draw
conclusion on whether any impacts on dolphins have been detected related to the
construction activities of the TM-CLKL Southern Connection Viaduct Section in
the quarterly EM&A reports, in which comparison on distribution, group size
and encounter rates of dolphins between the quarterly impact monitoring period
and baseline monitoring period will be made.
Daily 250 m marine mammal exclusion zone
monitoring was undertaken during the period of daytime marine works
activities. No sighting of Chinese White
Dolphin was recorded in May 2018 during the exclusion zone monitoring.
Passive Acoustic Monitoring (PAM) had been
decommissioned as no marine piling works was carried out outside the daylight
hours since September 2015.
Site
inspections were carried out on a weekly basis to
monitor the implementation of proper environmental pollution control and
mitigation measures under the Contract.
In the reporting month, five (5) site inspections were carried out on 2,
9, 16, 23 and 31 May 2018.
Key
observations during the site inspections are summarized in Table 2.14.
Table 2.14 Specific Observations Identified during the Weekly Site
Inspections in this Reporting Month
Inspection Date |
Environmental Observations |
Recommendations/ Remarks |
2 May 2018 |
Southern
Landfall (Portion A)(Portion S-c) Chemical containers were
observed not placed in drip tray. Stagnant water was
observed in the drip tray. General refuse should be
removed. |
Southern
Landfall (Portion A)(Portion S-c) The Contractor was reminded to
place chemical containers in drip tray. The Contractor was reminded to
clear stagnant water in the drip tray. The
Contractor was reminded to clear general refuse. |
9 May 2018 |
Viaduct E
(Pier E13CD) Wastewater in the drip
tray should be cleared. Chemical containers were
observed not placed in drip tray. Viaduct E Refuse in the gully
should be removed. |
Viaduct B
(Pier E13CD) The Contractor was reminded to clear wastewater
in the drip tray. The Contractor was reminded to
place chemical containers in drip tray. Viaduct E The Contractor was
reminded to remove refuse in the gully. |
16 May 2018 |
Viaduct C
(Pier C5) Chemical containers were
observed not placed in drip tray. Viaduct C
(Ramp C)(Area I) Stagnant water was
observed in the drip tray. |
Viaduct C
(Pier C5) The Contractor was reminded to
place chemical containers in drip tray. Viaduct C
(Ramp C)(Area I) The Contractor was reminded to
clear stagnant water in the drip tray. |
23 May 2018 |
Viaduct E (Pier
E7) Refuse in the gully
should be removed. Viaduct E
(Pier E10) Unauthorized chemical
containers should not be used to store chemicals and should be removed. Viaduct E
(Pier E11) General refuse should be
disposed of in the skip and removed regularly. |
Viaduct E
(Pier E7) The Contractor was reminded to
remove refuse in the gully. Viaduct E
(Pier E10) The Contractor was reminded to
remove unauthorized chemical containers. Viaduct E
(Pier E11) The Contractor was reminded to
remove general refuse on the deck. |
31 May 2018 |
Pak Mong (near
Pier B17) General refuse should be
disposed of in the skip. Viaduct E (Pier E10) Watering should be
implemented when breaking oversize concrete. Viaduct E (E11) The
opened cement bag should be covered by tarpaulin for dust suppression. |
Pak Mong (near
Pier B17) The Contractor was reminded to
dispose of the general refuse in the skip. Viaduct E (Pier E10) The Contractor was reminded to
provide watering when breaking concrete. Viaduct E
(Pier E11) The Contractor was reminded to
cover the opened cement bag by tarpaulin. |
The Contractor has rectified all of the observations
identified during environmental site inspections in the reporting month.
The Contractor has submitted application form for
registration as chemical waste producer under the Contract. Sufficient numbers of receptacles were
available for general refuse collection and sorting.
Wastes generated during this reporting period include
mainly construction wastes (inert and non-inert) and recyclable materials. Reference has been made to the waste flow
table prepared by the Contractor (Appendix M). The quantities of different types of wastes
are summarized in Table 2.15.
Table 2.15 Quantities of Different Waste Generated in the Reporting Period
Month/ Year |
Inert C&D Materials (a)
(m3) |
Imported Fill (m3) |
Inert Construction Waste Re-used (m3) |
Non-inert Construction Waste (b)
(kg) |
Recyclable Materials (c) (kg) |
Chemical Wastes (kg) |
Marine Sediment (m3) |
||
Category L |
Category M (Mp & Mf) |
Category H |
|||||||
May 2018 |
4,492 |
1,336 |
1,481 |
438,160 |
56 |
0 |
0 |
0 |
0 |
Notes: |
|||||||||
(a)
Inert construction wastes include hard rock and
large broken concrete, and materials disposed as public fill. (b)
Non-inert construction wastes include general refuse
disposed at landfill. (c)
Recyclable materials include metals, paper,
cardboard, plastics, timber, felled trees and others. |
The Contractor was advised to properly maintain on
site C&D materials and waste collection, sorting and recording system,
dispose of C&D materials and wastes at designated ground and maximize reuse/
recycle of C&D materials and wastes.
The Contractor was also reminded to properly maintain the site tidiness
and dispose of the wastes accumulated on site regularly and properly.
For chemical waste containers, the Contractor was
reminded to treat properly and store temporarily in designated chemical waste
storage area on site in accordance with the Code
of Practice on the Packaging, Labelling and Storage of Chemical Wastes.
The status of environmental licensing and permit is
summarized in Table 2.16 below.
Table 2.16 Summary of Environmental Licensing and Permit Status
License/ Permit |
License or Permit No. |
Date of Issue |
Date of Expiry |
License/ Permit Holder |
Remarks |
Environmental Permit |
EP-354/2009/D |
13 Mar 2015 |
N/A |
HyD |
Tuen
Mun- Chek Lap Kok Link |
Environmental Permit |
EP-353/2009/K |
11 Apr 2016 |
N/A |
HyD |
Hong
Kong Boundary Crossing Facilities |
Construction Dust Notification |
361571 |
5 Jul 2013 |
N/A |
GCL |
|
Construction Dust Notification |
362093 |
17 Jul 2013 |
N/A |
GCL |
For Area 23 |
Chemical Waste Registration |
5213-961-G2380-13 |
10 Oct 2013 |
N/A |
GCL |
Chemical waste produced in Contract No. HY/2012/07 (Area 1 adjacent to Cheng Tung Road, Siu Ho Wan) |
Chemical Waste Registration |
5213-961-G2380-14 |
10 Oct 2013 |
N/A |
GCL |
Chemical waste produced in Contract No. HY/2012/07 (Area 2 adjacent to Cheung Tung Road, Pak Mong
Village) |
Chemical Waste Registration |
5213-974-G2588-03 |
4 Nov 2013 |
N/A |
GCL |
Chemical waste produced in Contract No. HY/2012/07 (WA5 adjacent to Cheung Tung Road, Yam O) |
Chemical Waste Registration |
5213-951-G2380-17 |
12 Jun 2014 |
N/A |
GCL |
Viaducts A, B, C, D & E |
Construction Waste Disposal Account |
7017735 |
10 Jul 2013 |
N/A |
GCL |
- |
Construction
Waste Disposal Account |
7019470 |
3 Mar 2014 |
N/A |
GCL |
Vessel
CHIT Account |
Waste Water Discharge License |
WT00019017-2014 |
13 May 2014 |
31 May 2019 |
GCL |
Discharge for marine portion |
Waste Water Discharge License |
WT00019018-2014 |
13 May 2014 |
31 May 2019 |
GCL |
Discharge for land portion |
Construction Noise Permit for night
works and works in general holidays |
GW-RW0650-17 |
19 Dec 2017 |
18 Jun 2018 |
GCL |
General works at WA5 |
Construction Noise Permit for night works
and works in general holidays Construction Noise Permit for night
works and works in general holidays |
GW-RS0244-18 GW-RS0328-18 |
30 Mar 2018 30 Apr 2018 |
29 Sep 2018 29 Jun 2018 |
GCL GCL |
Broad Permit for Whole Site Areas Broad Permit for Segment Launching at
Land Portion |
Construction Noise Permit for night
works and works in general holidays Construction Noise Permit for night
works and works in general holidays |
GW-RS0411-18 GW-RS0064-18 |
26 May 2018 1 Feb 2018 |
31 May 2018 29 Jul 2018 |
GCL GCL |
Street lamp replacement at East Coast Road Pre-casted pile cap shell installation at E8-E13 |
|
|
|
|
|
|
In response to the site audit findings, the Contractors
carried out corrective actions.
A summary of the Implementation Schedule of
Environmental Mitigation Measures (EMIS) is presented in Appendix C. The necessary mitigation measures were implemented
properly for this Contract.
The landscape and visual (L&V) mitigation measures
were also monitored on weekly basis in the reporting period. The monitoring status is summarized in Appendix C.
Results for 1-hour TSP, 24-hour TSP and construction
noise monitoring complied with the Action/ Limit levels in the reporting
period.
One (1) Action Level of Dissolved Oxygen (DO) exceedance was recorded for water quality impact
monitoring in the reporting month. The exceedance were considered not related to this Contract upon
further investigation and the investigation report is presented in Appendix N.
One (1) Limit Level exceedance was observed for the
quarterly dolphin monitoring data between March and May 2018, whilst no
unacceptable impact from the construction activities of the TM-CLKL Southern
Connection Viaduct Section on Indo-Pacific humpback dolphin Sousa chinensis (i.e. Chinese White
Dolphin) was noticeable from general observations.
Cumulative statistics on exceedances is provided in Appendix N.
The Environmental Complaint Handling Procedure is provided in Figure 2.5.
There was no environmental complaint, notification of summons
or successful prosecution recorded in the reporting period.
Statistics on complaints, notifications of summons,
successful prosecutions are summarized in Appendix N.
As informed by the Contractor, the major works for
this Contract in June 2018 will be:
· Pier
construction;
· Re-alignment
of Cheung Tung Road;
· Road
works along North Lantau Highway;
· Installation
of pier head and deck segments;
· Asphalt
paving;
· Construction
of sign gantries, light poles and street furniture;
· Parapets
and barriers installation; and
· Slope
work of Viaducts A, B, C & D.
Potential environmental impacts arising from the above
upcoming construction activities in the next reporting month of June 2018 are
mainly associated with dust, noise, marine water quality, marine ecology and
waste management issues.
The tentative schedules for environmental
monitoring in June 2018 are provided in Appendix F.
This Fifty-fifth Monthly EM&A Report presents the
findings of the EM&A activities undertaken during the period from 1 to 31
May 2018 in accordance with the Updated EM&A Manual and the requirements of
the Environmental Permits (EP-354/2009/D and EP-353/2009/K).
Air quality (1-hour TSP and 24-hour TSP), noise, water
quality (DO, turbidity and SS) and dolphin monitoring were carried out in the
reporting month. Results for air quality
and noise monitoring complied with the Action and Limit levels in the reporting
period.
One (1) Action Level of Dissolved Oxygen (DO)
exceedance was recorded for water quality impact monitoring in the reporting
month.
No Chinese White Dolphins were sighted during the two
sets of monitoring surveys in May 2018. One
(1) Limit Level exceedance was observed for the quarterly dolphin monitoring data
between March and May 2018, whilst no
unacceptable impact from the construction activities of the TM-CLKL Southern
Connection Viaduct Section on Indo-Pacific humpback dolphin Sousa chinensis (i.e. Chinese White
Dolphin) was noticeable from general observations.
Environmental site inspection was carried out five (5)
times in May 2018. Recommendations on
remedial actions were given to the Contractor for the deficiencies identified
during the site audits.
There was no environmental complaint, notification of
summons or successful prosecution recorded in the reporting period.
The ET will keep track on the
construction works to confirm compliance of environmental requirements and the
proper implementation of all necessary mitigation measures.