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Revision History
Rev. |
Description
of Modification |
Date |
0 |
First Issue for Comments |
23
June 2021 |
1 |
Revision
according to IEC’s comments |
28
June 2021 |
2 |
Revision
according to the Contractor and IEC’s comments |
29
June 2021 |
3 |
Revision
according to the Contractor and IEC’s comments |
29
June 2021 |
CONTENTS
1.4.
Summary of Construction
Works
1.5.
Summary of
Environmental Status
2.3.
Impact Monitoring
Methodology
2.5. Monitoring Results and
Observations
3.3. Sampling / Testing Protocols
3.4. Laboratory Measurement and
Analysis
3.7. Sampling Depths &
Replication
3.10. Monitoring
results and observations
5. Summary of Monitoring Exceedance,
Complaints, Notification of Summons and Prosecutions
8. Conclusions and Recommendations
Appendix A |
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Appendix B |
Summary
of Implementation Status of Environmental Mitigation |
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Appendix C |
Impact
Monitoring Schedule of this and next Reporting Period |
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Appendix D |
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Appendix E |
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Appendix F |
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Appendix G |
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Appendix
H |
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Works Description |
Location |
Preparation
works before pile pipe works at Look out Point & Landing Facility Footing construction for the new viewing platform |
|
·
Construction
dust and noise generation from construction works and excavation works
·
Waste
generation from the construction activities
·
Dust suppression by
regular wetting and water spraying for construction works
·
Reduction
of noise from equipment and machinery on-site
·
Sorting
and storage of general refuse and construction waste
Works Description |
Location |
Install pipe pile wall
at Lookout Point & Landing Facilities |
Lookout Point and
Landing Facility Construction Area |
Marine GI works prior to
piling construction at Breakwater |
Breakwater Area |
Removal of rock armour
within Landing Facility and Breakwater areas |
Landing Facility and
Breakwater Construction Area |
Structural monitoring
survey to the nearby existing structures |
Existing Structures to
be Potential Effected by Construction
Activities |
Demolition of Gabion
Wall |
Near
Lei Yue Mun Rest Garden |
Construction
works for new planter 1, 2, 3 & 4 |
Proposed
Pavilion Area |
Excavation
works for footing of new wind turbine |
Proposed
Pavilion Area |
Excavation
works for trench of laying cable pipes |
Proposed
Pavilion Area |
Installation
works of hoarding light |
Proposed
Pavilion Area |
·
Construction dust and noise generation from excavation and construction
works
·
Waste generation from construction
activities
·
Dust suppression by regular wetting and
water spraying for construction works
·
Reduction of noise from equipment and
machinery on-site
·
Sorting and storage
of general refuse and construction waste
Civil Engineering and
Development Department (CEDD) has contracted Concentric - Hong Kong River Joint
Venture (CHKRJV) to carry out the Construction of Lei Yue Mun Public Landing
Facility under Contract No. CV/2020/09; and Architectural Services Department
(ArchSD) has contracted Milestone Builder Engineering Limited to carry out
the development of a waterfront promenade and related improvement works
under Contract No. SS J521 for the Lei Yue Mun Waterfront Enhancement Project (the Project).
Acuity Sustainability Consulting Limited
(ASCL) is commissioned by CEDD to undertake the Environmental Team (ET)
services as required and/or implied, both explicitly and implicitly, in the
Environmental Permit (EP), Environmental Impact Assessment Report (EIA Report)
(Register No. AEIAR-219/2018) and Environmental Monitoring and Audit Manual
(EM&A Manual) for the Project; and to carry out the Environmental
Monitoring and Audit (EM&A) programme in fulfillment of the EIA Report’s
EM&A requirements under Contract No. PI 2/2020.
Pursuant to the Environmental Impact
Assessment Ordinance (EIAO), the Director of Environmental Protection granted
the Environmental Permit (No. EP-564/2018) to CEDD for the Project.
This is the 1st Monthly
EM&A Report for the Project which summarizes the key findings of the
EM&A programme during the reporting period from 1 May to 31 May 2021.
The
Project Organization structure for Construction Phase is presented in Figure
1.1. The key personnel’s’ contacts are
presented in Table 1.1 and Table 1.2.
Figure
1.1 Project Organization Chart
Table 1.1 Key
Personnel’s’ Contact for the Construction of a Public Landing Facility and
Improvement Works to Existing Lookout Points and Viewing Platform
Party |
Position |
Name |
Phone |
Civil
Engineering and Development Department |
Engineer |
Ms.
Lam Sau Lai, Katy |
2762
5044 |
ANewR |
Independent
Environmental Checker |
Mr.
Choi Pui Sum, James |
2618
2831 |
Acuity
Sustainability Consulting Limited |
Environmental
Team |
Mr.
Li Wai Ming, Kevin |
2698
6833 |
Concentric
- Hong Kong River Joint Venture |
Contractor |
Mr.
Lam Tat Shing |
9655
5486 |
Table 1.2 Key
Personnel’s’ Contact for the Development of a Waterfront Promenade and Related
Improvement Works
|
|||
Party |
Position |
Name |
Phone |
Architectural
Services Department |
Project
Manager |
Mr.
C.Y. Chan |
2867
3850 |
ANewR |
Independent
Environmental Checker |
Mr.
Choi Pui Sum, James |
2618
2831 |
Acuity
Sustainability Consulting Limited |
Environmental
Team |
Mr.
Li Wai Ming, Kevin |
2698
6833 |
Milestone
Builder Engineering Ltd. |
Environmental
Officer |
Ms.
Emily Yim |
6311
1571 |
Details of
the major construction activities undertaken in this reporting period are shown
as below. The construction programme is presented in Appendix A.
Key activities
carried out in this reporting period for the Project included the followings:
Location |
|
Preparation
works before pile pipe works at Look out Point & Landing Facility |
Lookout
Point and Landing Facility Construction Area |
Footing construction for the new viewing platform |
Proposed
Pavilion Area |
A summary of the valid permits, licences,
and/or notifications on environmental protection for this Project is presented
in Table 1.3.
Table
1.3 Summary of the Status of Valid Environmental
Licence, Notification, Permit and Documentations for
the Construction of a Public Landing Facility and Improvement Works to Existing
Lookout Points and Viewing Platform
Permit/ Licenses/
Notification |
Reference |
Validity Period |
Environmental Permit |
EP-564/2018 |
Throughout the Contract |
Notification of Construction Works under the Air Pollution Control
(Construction Dust) Regulation (Form NA) |
Ref. No.: 463353 |
Throughout the Contract |
Chemical Waste Producer Registration |
5213-298-C3752-02 |
Throughout the Contract |
Billing Account for Disposal of Construction Waste |
7039364 |
Throughout the Contract |
Table 1.4 Summary of the Status of Valid Environmental Licence,
Notification, Permit and Documentations for the Development of a Waterfront
Promenade and Related Improvement Works
Permit/ Licenses/ Notification |
Reference |
Validity Period |
Environmental Permit |
EP-564/2018 |
Throughout the Contract |
Notification of Construction Works under the Air
Pollution Control (Construction Dust) Regulation (Form NA) |
Ref. No.: 467619 |
Throughout the Contract |
Chemical Waste Producer Registration |
5312-298-M2939-02 |
Throughout the Contract |
Billing Account for Disposal of Construction Waste |
7039353 |
Throughout the Contract |
The status for all environmental aspects is presented in Table 1.5.
Table 1.5 Summary
of Status for Key Environmental Aspects under the EM&A Manual
Other than the EM&A work by ET, environmental
briefings, trainings and regular environmental management meetings were
conducted, in order to enhance environmental awareness and closely monitor the
environmental performance of the contractors.
The EM&A programme has been implemented
in accordance with the recommendations presented in the approved EIA Report and
the EM&A Manual. A summary of implementation status of the environmental
mitigation measures for the construction phase of the Project during the
reporting period is provided in Appendix
B.
To ensure no adverse noise impact, noise
monitoring is recommended to be carried out within 300m radius from the nearby
noise sensitive receivers (NSRs), during construction phase. The NSRs selected
as monitoring station are (i) NM1 – Village house in Lei Yue Mun Hoi Pong Road
Central, (ii) NM2-A – No.79B, Lei Yue Mun Hoi Pong Road East, (iii) NM3 –
Jockey Club Lei Yue Mun Plus and (iv) NM4 – No. 21C, Lei Yue Mun Hoi Pong Road
East respectively.
In accordance with the
EM&A Manual, baseline noise level at the
noise monitoring stations were established as presented in the Baseline
Monitoring Report. Impact noise monitoring was conducted once per week in the
form of 30-minutes measurements Leq, L10 and L90 levels recorded at each
monitoring station between 0700 and 1900 on normal weekdays.
Three (3) sessions of noise monitoring were carried out at the monitoring locations
sited at LYM in the reporting month. The results
are presented in Appendix
F.
Construction noise level
were measured in terms of the A-weighted equivalent continuous sound pressure
level (LAeq). Leq 30min was used as the monitoring parameter for the
time period between 0700 and 1900 on normal weekdays. Table 2.1 summarizes the monitoring
parameters, frequency and duration of the impact noise monitoring.
Table
2.1 Noise Monitoring Parameters, Time, Frequency
and Duration
Time |
Duration |
Interval |
Parameters |
Daytime: 0700-1900 |
Day time: 0700-1900 (during normal weekdays) |
Continuously in Leq 5min/Leq 30min (average of
6 consecutive Leq 5min) |
Leq 30min L10 30min & L90
30min |
The monitoring locations should normally be made at a point 1m from
the exterior of the NSRs building façade and be at a position 1.2m above the
ground. A correction of +3dB(A) should be made to the free-field measurements.
According to the environmental findings
detailed in the EIA report and Baseline Monitoring Report, the designated
locations for the construction noise monitoring are listed in Table 2.2
below.
Table
2.2 Noise Monitoring Locations
Station |
Noise Monitoring Stations |
Monitoring Location |
Position |
NM1 |
Village house in Lei Yue Mun Hoi Pong
Road Central |
Pedestrian Road on Ground
Floor |
1 m from facade |
NM2 |
No.81, Lei Yue Mun Hoi Pong Road East |
Pedestrian Road on Ground
Floor |
1 m from facade |
NM3 |
Jockey Club Lei Yue Mun P lus |
Fenced Road on Ground Floor |
1 m from facade |
NM4 |
No. 21C, Lei Yue Mun Hoi Pong
Road East |
Fenced Road on Ground Floor |
1 m from facade |
The original construction
noise monitoring station NM2 was selected at the façade of No. 81 of Lei Yue
Mun Hoi Pong Road East. However, the residents of the premises at No. 81 of Lei
Yue Mun Hoi Pong Road East do not allow the setting up of the construction
noise monitoring station NM2. No. 79B, Lei Yue Mun Hoi Pong Road East, was
proposed as the alternative noise monitoring location for set up of
construction noise monitoring station named as NM2-A.
A Proposal for
Alternative Noise Monitoring Station, which was certified by the ET Leader and
verified by the IEC, has been prepared to conclude that the alternative
construction noise monitoring station NM2-A could conform to relevant
requirements as set out in the EM&A Manual, namely:
·
locate close to the major site
activities which are likely to have noise impacts;
·
locate close to the most affected
existing NSRs; and
·
take into account the possibility
of minimizing disturbance to occupants at the NSRs during monitoring.
The Proposal for Alternative
Noise Monitoring Station NM2-A has
been approved by EPD on 16 April 2021.
The latest locations
for the construction noise monitoring are listed in Table 2.3.
Table 2.3
Updated Noise Monitoring
Stations for Baseline and Impact Monitoring
Station |
Noise Sensitive Receiver |
Monitoring Location |
Position |
NM1 |
Village house in Lei Yue Mun
Hoi Pong Road Central |
Pedestrian Road on Ground
Floor |
1 m from facade |
NM2-A |
No.79B, Lei Yue Mun Hoi Pong
Road East |
Pedestrian Road on Ground
Floor |
1 m from facade |
NM3 |
Jockey Club Lei Yue Mun Plus |
Fenced Road on Ground Floor |
1 m from facade |
NM4 |
No. 21C, Lei Yue Mun Hoi Pong
Road East |
Fenced Road on Ground Floor |
1 m from facade |
The location of all original construction noise
monitoring stations and the alternative construction noise monitoring station
are shown in Figure 2.1.
Figure
2.1 Noise Monitoring Locations |
Integrated sound
level meter shall be used for the noise monitoring. The meter shall be in
compliance with the International Electrotechnical Commission Publications 651:
1979 (Type 1) and 804: 1985 (Type 1) specifications. 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 levels before and after the noise measurements agree to within 1.0
dB(A). Calibration certificates of the instruments used are shown at Appendix E.
Noise measurements shall not be made in the
presence of 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.
Table
2.4 Impact Noise Monitoring Equipment
The Action/Limit Levels are in line with
the criteria of Practice Note for Professional Persons (ProPECC PN 2/93) “Noise
from Construction Activities – Non-statutory Controls” and Technical Memorandum
on Environmental Impact Assessment Process issued by HKSAR Environmental
Protection Department [“EPD”] under the Environmental Impact Assessment
Ordinance, Cap 499, S.16 are presented in Table 2.5.
Table 2.5 Action
and Limit Levels for Noise per EM&A Manual
Time Period |
Action |
Limit (dB(A)) |
0700-1900
on normal weekdays |
When one
documented complaint is received from any one of the noise sensitive
receivers |
75 dB(A) for residential areas; 70
dB(A) for school; and 65
dB(A) during examination period |
Notes: Limits specified in the GW-TM and IND-TM for construction and
operation noise, respectively.
If
exceedances were found during noise monitoring, the actions in accordance with
the Event and Action Plan shall be carried out according to Appendix D.
Referring to EM&A manual Section
4.6.1.1 construction noise monitoring should be carried out when there are
project-related construction activities undertaken within a radius of 300m from
the monitoring stations. Three (3) sessions of noise monitoring were carried
out at the monitoring locations sited at LYM in the reporting month. The below Table
2.6 summarized the results of the
monitoring.
Table 2.6 Summary
of Noise Monitoring Results in the Reporting Month
Location |
Noise in dB(A) |
Leq 30min Daytime (7:00-19:00 on normal weekdays) |
|
NM1 |
54.9
– 57.3 |
NM2-A |
63.5
– 65.4 |
NM3 |
60.3
– 60.5 |
NM4 |
60.9
– 62.0 |
As identified in the EIA Report, suspended
sediment is the most critical water quality parameter caused by the dredging
works. Marine water quality monitoring should be carried out during the
dredging and filling operation to ensure that any unacceptable increase in
suspended solids / turbidity and decrease in dissolved oxygen due to the
dredging activities could be readily detected and timely action be taken to
rectify the situation. In addition, baseline water quality monitoring was
conducted prior to the commencement of marine construction activities. The
following Section provides details of the water quality monitoring to be
undertaken by the Environmental Team (ET). The water quality monitoring
programme will be carried out to allow any deteriorating water quality to be
readily detected and timely action taken to rectify the situation.
As the construction of marine-based works are
scheduled to commence in July 2021 tentatively, no water quality monitoring was
conducted in the reporting month.
The parameters that have been selected for
measurement in situ and in the laboratory are those that were either determined
in the EIA to be those with the most potential to be affected by the
construction works or are a standard check on water quality conditions.
Parameters to be measured in the impact monitoring
are listed in Table 3.1.
Table
3.1 Parameters measured in the marine
water quality monitoring
Parameters |
Unit |
Abbreviation |
In-situ
measurements |
||
Dissolved
oxygen |
mg/L |
DO |
Temperature |
oC |
- |
pH |
- |
- |
Turbidity |
NTU |
- |
Salinity |
mg/L |
- |
Laboratory
measurements |
||
Suspended
Solids |
mg/L |
SS |
For water quality monitoring, the following
equipment will be used:
Dissolved Oxygen and Temperature
Measuring Equipment - The instrument will be a
portable, weatherproof dissolved oxygen measuring instrument complete with
cable, sensor, comprehensive operation manuals, and will be operable from a DC
power source. It will be capable of measuring: dissolved oxygen levels in the
range of 0 - 20 mg/L and 0 - 200% saturation; and a temperature of 0 - 45
degrees Celsius. It shall have a membrane electrode with automatic temperature
compensation complete with a cable of not less than 35 m in length. Sufficient
stocks of spare electrodes and cables shall be available for replacement where
necessary (e.g. YSI model 59 DO meter, YSI 5739 probe, YSI 5795A submersible
stirrer with reel and cable or an approved similar instrument).
Turbidity Measurement Equipment - The instrument will be a portable, weatherproof
turbidity-measuring unit complete with cable, sensor and comprehensive
operation manuals. The equipment will be operated from a DC power source, it
will have a photoelectric sensor capable of measuring turbidity between 0 -
1000 NTU and will be complete with a cable with at least 35 m in length (for
example Hach 2100P or an approved similar instrument).
pH Measurement Instrument - The instrument should consist of a potentiometer, a glass
electrode, a reference electrode and a temperature-compensating
device. It should be readable to 0.1 pH in a range of 0 to
14. Standard buffer solutions of at least pH 7 and pH 10 should be
used for calibration of the instrument before and after use.
Salinity Measurement Instrument - A portable salinometer capable of measuring salinity in the range
of 0 - 40 ppt will be provided for measuring salinity of the water at each
monitoring location.
Sample Containers and Storage
- Water samples for SS should be stored in high density polythene bottles with
no preservative added, packed in ice (cooled to 4 °C without being frozen)
and delivered to the laboratory and analyzed
as soon as possible after collection. Sufficient volume of samples should be
collected to achieve the detection limit.
Water Depth Gauge – A portable, battery-operated echo sounder (for example Seafarer
700 or a similar approved instrument) will be used for the determination of
water depth at each designated monitoring station. This unit will preferably be
affixed to the bottom of the work boat if the same vessel is to be used
throughout the monitoring programme. The echo sounder should be suitably
calibrated. The ET shall seek approval for their proposed equipment with the
client prior to deployment.
Positioning Device – A Global Positioning System (GPS) shall be used during monitoring
to allow accurate recording of the position of the monitoring vessel before
taking measurements. The Differential GPS, or equivalent instrument, should be
suitably calibrated at appropriate checkpoint (e.g. Quarry Bay Survey Nail) to
verify that the monitoring station is at the correct position before the water
quality monitoring commence.
Water Sampling Equipment - A water sampler, consisting of a PVC or glass cylinder of not
less than two litres, which can be effectively sealed with cups at both ends,
will be used (e.g. Kahlsico Water Sampler 13SWB203 or an approved similar instrument).
The water sampler will 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.
All in situ monitoring instruments will be
checked, calibrated and certified by a laboratory accredited under HOKLAS or
any other international accreditation scheme before use, and subsequently
re-calibrated at monthly intervals throughout the stages of the water quality
monitoring. Responses of sensors and electrodes will be checked with certified
standard solutions before each use.
On-site calibration of field equipment
shall follow the “Guide to On-Site Test Methods for the Analysis of Waters”, BS
1427: 2009. Sufficient stocks of spare parts shall be maintained for
replacements when necessary. Backup monitoring equipment shall also be made
available so that monitoring can proceed uninterrupted even when equipment is
under maintenance, calibration etc.
All laboratory work shall be carried out in
a HOKLAS accredited laboratory. Sufficient volume of each water sample shall be
collected at the monitoring stations for carrying out the laboratory analyses.
Using chain of custody forms, collected water samples will be transferred to an
HOKLAS accredited laboratory for immediate processing. The determination work
shall start within 24 hours after collection of the water samples. The
laboratory measurements shall be provided to the client within 5 working days
of the sampling event. Analytical methodology and sample preservation of other
parameters will be based on the latest edition of Standard Methods for the
Examination of Waste and Wastewater published by APHA, AWWA and WPCF and
methods by USEPA, or suitable method in accordance with requirements of HOKLAS
or another internationally accredited scheme.
Detailed testing methods, pre-treatment
procedures, instruments use, Quality Assurance / Quality Control (QA/QC)
details (such as blank, spike recovery, number of replicate samples per batch,
etc.), detection limit and accuracy were submitted to EPD for approval on 3
February 2021 prior to the commencement of monitoring programme. EPD may also
request the laboratory to carry out analysis of known standards provided by EPD
for quality assurance. The QA / QC shall be in accordance with the requirements
of HOKLAS or international accredited scheme. The QA/ QC results shall be
reported. The testing methods and related proposal were checked and certified
by IEC before submission to EPD for approval.
Parameters for laboratory measurements,
their standard methods and their detection limits are presented in Table 3.2.
Table 3.2 Laboratory measurements, standard methods and
corresponding detection limits of marine water quality monitoring
Parameter |
Standard Method |
Detection Limit |
Accuracy |
Suspended Solids (mg/L) |
APHA 2540D |
1.0* |
±17% |
Remark *: Albeit the selected HOKLAS accredited
laboratories’ standard testing method of total suspended solid according to
APHA Method 2540D is capable of reporting the results to 1 mg/L, the laboratory
advised that results reported between 1 and 2 mg/L shall be considered to be
used as reference value and receive no HOKLAS accreditation for this particular
range of result
If exceedances were found during
water monitoring, the actions in accordance with the Event and Action Plan
shall be carried out according to Appendix G.
The water quality monitoring locations for
baseline are in accordance to the EM&A Manual and detailed in Table 3.3
below. The water quality monitoring schedule should
be submitted to EPD at least 1 week before the first day of the monitoring
month.
Table 3.3 Location of Water
Quality Monitoring Station
Station |
Easting |
Northing |
Description |
C1 |
842134 |
816765 |
Control Station |
C2 |
842946 |
816172 |
Control Station |
M1 |
842605 |
816433 |
Coral Communities (Impact Monitoring Station) |
M2 |
842329 |
816615 |
100m away from the dredging site (Impact Monitoring Station) |
M3 |
842639 |
816410 |
Coral Communities (Impact Monitoring Station) |
M4 |
842515 |
816878 |
Sam Ka Tsuen Typhoon Shelter (Impact Monitoring Station) |
Figure 3.1 Water quality monitoring locations under
EM&A Manual
During periods when there are dredging or
filling works, impact monitoring should be undertaken at the monitoring
stations as shown in Figure 3.1 and Table 3.3 three days per week
during the construction phase after the commencement of marine construction
works and dredging or filling activities. Monitoring at each station would be
undertaken at both mid-ebb and mid-flood tides on the same day. The interval between
two sets of monitoring would not be less than 36 hours. The monitoring
frequency would be increased in the case of exceedances of Action/Limit Levels
if considered necessary by ET. Monitoring frequency would be maintained as far
as practicable.
For water
quality monitoring, each station will be sampled and measurements/ water
samples will be taken at three depths, 1 m below the sea surface, mid-depth and
1 m above the seabed. For stations that are less than 3 m in depth, only the
mid depth sample shall be taken. For stations that are less than 6 m in depth,
only the surface and seabed sample shall be taken. For in situ measurements,
duplicate readings shall be made at each water depth at each station. Duplicate
water samples shall be collected at each water depth at each station.
The Action and Limit Levels have been set
based on the derivation criteria specified in the EM&A Manual, as shown in Table
3.4 below. Based on the baseline water quality monitoring data and the
derivation criteria specified in Table 3.4, the Action/Limit Levels have
been derived and are presented in Table 3.5.
The ET of the Project had conducted the
baseline water monitoring between 15 April 2021 to 11 May 2021 at all six designated
monitoring stations (i.e. C1, C2, M1, M2, M3 and M4). The monitoring results was presented in
Baseline Water Quality Monitoring Report separately.
The commencement of marine construction
activities for the Project is expected to be commenced in July 2021.
Table 3.4Criteria of Action and Limit Levels for Water
Quality
Parameters |
Action |
Limit |
During the Dredging and Filling Operation of the Project |
||
DO in mg/L |
Surface and Middle ≤5%-ile of baseline data
for surface and middle layers Bottom ≤5%-ile of baseline data
for bottom layer |
Surface
and Middle ≤4 mg/L or 1%-ile of
baseline data for surface and middle layers Bottom ≤2 mg/L or 1%-ile of
baseline data for bottom layer |
SS in mg/L (Depth-averaged) |
≥ 95 %-ile of baseline data or 120% of control station’s SS at the
same tide of the same day |
≥ 99 %-ile of baseline data or 130% of control station’s SS at the
same tide of the same day and specific sensitive receiver water quality requirements
(e.g. required SS level for concerned seawater intakes) |
Turbidity in NTU (Depth-averaged) |
≥ 95 %-ile of baseline data or 120% of control station’s SS at the
same tide of the same day |
≥ 99 %-ile of baseline data or 130% of control station’s SS at the
same tide of the same day |
Table 3.5 Derived
Action and Limit Levels for Water Quality
Parameters |
Action |
Limit |
During the Dredging and Filling Operation of the Project |
||
DO in mg/L |
Surface and Middle 7.95 mg L-1 Bottom 7.91 mg L-1 |
Surface
and Middle 4 mg L-1 Bottom 2 mg L-1 |
SS in mg/L (Depth-averaged) |
6.73 mg L-1 or
120% of control station’s SS at the same tide of the same day |
17.60 mg L-1 or
130% of control station’s SS at the same tide of the same day and specific
sensitive receiver water quality requirements (e.g. required SS level for
concerned seawater intakes) |
Turbidity in NTU (Depth-averaged) |
7.42 NTU or 120% of
control station’s SS at the same tide of the same day compared with
corresponding data from control station |
7.79 NTU or 130% of
control station’s SS at the same tide of the same day compared with
corresponding data from control station |
Notes:
i.
"Depth-averaged" is calculated by taking the
arithmetic means of reading of all three depths.
ii.
For DO, non-compliance of the water quality limits
occurs when monitoring result is lower than the limits.
iii.
For Turbidity, SS and Salinity, non-compliance of the
water quality limits occurs when monitoring result is higher than the limits.
No water quality monitoring was conducted
in the reporting period because marine-based works was
scheduled to commence in July 2021.
The waste generated from this Project
includes inert construction and demolition (C&D) materials, and non-inert
C&D materials. Non-inert C&D materials are made up of general refuse,
vegetative wastes and recyclable wastes such as plastics and paper/cardboard
packaging waste. Steel materials generated from the project are also grouped
into non-inert C&D materials as the materials were not disposed of with
other inert C&D materials. With reference to relevant handling records and
trip tickets of this Project, the quantities of different types of waste
generated in the reporting month are presented in
Table 4.1.
Table 4.1 Quantities
of Waste Generated from the Project during 2021
Three (3) sessions of noise monitoring was
carried out at the monitoring locations sited at LYM in the reporting month.
No noise-related exceedance was recorded in
the reporting period.
No notification of summons and prosecution
was received in the reporting period.
Statistics on complaints and regulatory
compliance are summarized in Appendix H.
Site inspections
were carried out on a weekly basis to monitor the implementation of proper
environmental pollution control and mitigation measures under the Contract. In
the reporting period, site inspections with CEDD
and ArchSD were carried out on 13, 20 and 27 May 2021. A joint site inspection with IEC was carried out on 20 May
2021.
Environmental deficiencies
were observed during weekly site inspection. Key observations during the site
inspections and during the reporting period are summarized in Table 7.1.
Table 6.1 Site Observations
Date |
Environmental
Observations |
Follow-up Status |
13 May 2021 |
Observation(s) and Recommendation(s) 1.
EP shall be displayed at the
proposed pavilion area’s entrance. |
EP
was displayed at the proposed pavilion area’s
entrance. |
20 May 2021 |
Observation(s) and Recommendation(s) 1.
At viewing platform, drip tray for placing chemical
in-use was broken, the drip tray should be replaced. |
An
appropriate drip tray was used. |
27 May 2021 |
Observation(s) and Recommendation(s) 1. No major observations were reported on the respective day. |
Nil. |
According to the EIA Study Report,
Environmental Permit, contract documents and EM&A Manual, the mitigation
measures detailed in the documents should be implemented as much as practical
during the reporting period. An updated Implementation Status of Environmental
Mitigation Measures (EMIS) is provided in Appendix
B.
Works to be undertaken in the next reporting
month are:
Works
Description |
Location |
|
Install
pipe pile wall at Lookout Point & Landing Facilities |
Lookout
Point and Landing Facility Construction Area |
|
Marine
GI works prior to piling construction at Breakwater |
Breakwater
Area |
|
Removal
of rock armour within Landing Facility and Breakwater areas |
Landing
Facility and Breakwater Construction Area |
|
Structural
monitoring survey to the nearby existing structures |
Existing
Structures to be Potential Effected by Construction Activities |
|
Demolition
of Gabion Wall |
Near
Lei Yue Mun Rest Garden |
|
Construction
works for new planter 1, 2, 3 & 4 |
Proposed
Pavilion Area |
|
Excavation
works for footing of new wind turbine |
Proposed
Pavilion Area |
|
Excavation
works for trench of laying cable pipes |
Proposed
Pavilion Area |
|
Installation
works of hoarding light |
Proposed
Pavilion Area |
|
The major
environmental impacts brought by the above construction works will include:
·
Construction dust and noise generation from
excavation and construction works
·
Waste generation
from construction activities
The key
environmental mitigation measures for the Project in the coming reporting
period associated with the above construction works will include:
·
Dust suppression by
regular wetting and water spraying for construction works
·
Reduction of noise
from equipment and machinery on-site
·
Sorting and storage
of general refuse and construction waste
Referring to
EM&A Manual Section 4.6.1.1, the impact noise monitoring should be carried
out at all the designated monitoring stations when there are project-related
construction activities undertaken within a radius of 300m from the monitoring
stations.
This is the 1st Monthly EM&A Report for the Project
which summarizes the key findings of the EM&A programme during the
reporting period from 1 May to 31 May 2021, in accordance with the EM&A
Manual and the requirement under EP-564/2018.
Three (3) sessions of noise monitoring were
carried out at the monitoring locations sited at LYM in the reporting month
No water quality monitoring was conducted
in the reporting period due to no marine-based works was conducted.
No exceedance of Action or Limit Level was
recorded.
Weekly environmental site inspection was
conducted during the reporting period. No major deficiency was observed during
site inspection. The environmental performance of the project was therefore
considered satisfactory.
No environmental complaint was received in
the reporting period.
No notification of summons or prosecution
was received since commencement of the Contract.
Agreed with the EIA
prediction in Section 14.2.4.4, with the adoption of good site practice, quiet
PME and noise barriers/enclosure, the noise levels at all the representative
NSRs complied with the EIAO-TM noise criteria. The comparison between the
EM&A data in the reporting month and the most updated noise level
prediction as presented in the Noise Mitigation Plan (NMP) is presented in Table
8.1.
Table 8.1 Comparison between the EM&A Data in
the Reporting Month and the Updated Noise Level Predictions
EIA
Noise Assessment Point (NAP) |
Prediction
[dB(A)] |
EM&A
Monitoring Station |
Noise
Levels [db(A)] |
HPRC
V1 |
62-72 |
NM1 |
54.9-57.3 |
HPRE
75B* |
55-75 |
NM2-A |
63.5-65.4 |
LYMP |
70 |
NM3 |
60.3-60.5 |
HPRE
21C |
67-75 |
NM4 |
60.9-62.0 |
*NM2-A is located between
NAPs HPRE 75B and HPRE 81, with lack of data in the NMP, the EIA prediction was
used instead
The ET will keep track on the construction
works to confirm compliance of environmental requirements and the proper
implementation of all necessary mitigation measures.