


|
|
Table 3‑1 Air Quality Monitoring Equipment
Table 3‑2 Air Quality Monitoring Locations
Table 3‑3 Action & Limit Levels for Air
Quality
Table 3‑4 Event/Action Plan for Air Quality
Table 3‑5 Noise Monitoring Equipment
Table 3‑6 Noise Monitoring Locations
Table 3‑7 Action & Limit Levels for Noise
Table 3‑8 Event/Action Plan for Noise
Table 3‑9 Water Quality Monitoring Equipment
Table 3‑10 Water Quality Monitoring Locations
Table 3‑11 Action/Limit Levels for Water Quality
Table 3‑12 Event/Action Plan for Water Quality
Table 4-1 Air
Quality Monitoring Results
Table 4-2 Noise
Monitoring Results
Table 4-3 Summary
of Exceedances for I-1
Table 4-4 Summary
of Exceedances for I-2
Table 4-5 Summary
of Exceedances for I-3
Table 4-6 Water
Quality Monitoring Results
Table 4-7 Summary
of Project-Related Exceedances
Table 5-1 Waste Generated in August 2009
Table 6-1 Site
Inspection by ET
Table 7-1 Cumulative
Statistic of Environmental Complaint
Table 8-1 Cumulative
Statistics of Notification of Summons and Successful Prosecutions
|
Appendixes |
|
|
Appendix A Site Map and Works Area
Appendix C Construction Programme
Appendix D Implementation Status of
Environmental Mitigation Measures
Appendix E Status of License and Permit
Appendix F Calibration Certificates
Appendix G Monitoring Locations
Appendix J Interim Notifications of
Environmental Quality Limits Exceedances
2.
According
to the EM&A Manual, there are four designated air quality monitoring
locations, five designated noise monitoring locations and four water quality
monitoring locations during the construction phase: (i) Sik Sik Yuen Ho Fung
College (ASR 1, NSR 1 and Intake I-1); (ii) Hong Hoi Chee Hong Temple (ASR 3,
NSR 3 and Intake I-2); (iii) Squatters (NSR 6 and Intake I-3); (iv) Beach Tower
(Long Beach Gardens) (ASR 8, NSR 8 and Outfall O-1); and (v) Greenview Terrace
(Block 1) (ASR 9, NSR 9 and Outfall O-1).
3.
During the non restricted
hours, major construction activities undertaken by the Contractor at TWDT
included site cleaning and tidying, tree transplanting and breaking up exiting
boulder at I-1, I-2, I-3 and Outfall; drilling rig at I-3 and Outfall; soil
nailing at I-1, I-3 and Outfall; formation of access road at I-3 and
Outfall; erosion control mat and green wire mesh at Outfall; Excavation and
Lateral Support (ELS) at I-1; construction of skin wall at I-3; and
construction of steel platform at I-2. No construction activities
were carried out during restricted hours.
4.
No
exceedance has been recorded for air quality during the reporting month. For
noise monitoring, no exceedance of Limit level was recorded, however, five
environmental complaints on noise trigger the excceedances of Action Levels.
5.
No water quality monitoring was done on 12 August 2009 due to thunderstorm
warning. Exceedances for water
quality monitoring are summarized in the following table:
|
Parameter |
Action Level Exceedance |
Limit Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
One recorded at I-1 on 28 August |
Two recorded at I-1 and I-2 on 14 August |
6.
The
exceedances were considered not to be project-related as no direct disturbance
was observed contributed by the project construction activities. Detail interpretation
could be referred to Section 4.3 of this report.
7.
The status
of waste generation in the reporting month are:
·
A total of
6,403.3 m3 C&D material was disposed of to public fill at Tuen
Mun and 2, 695 m3 inert C&D materials were reused in other
Contracts. Detail information could be referred to Section 5.1.1 of this
report.
·
About 11.7
m3 general waste was disposed of to NENT Landfill;
·
No
paper/cardboard packaging was recycled;
·
Metals was
not generated in the reporting month; and
·
No plastic
waste and chemical waste were disposed of in the reporting month
8.
In this
reporting month, two site inspections and one monthly site audit were carried
out by ET and Independent Environmental Checker (IEC) respectively, to ensure
proper implementation of environmental mitigation measures specified in the
EM&A Manual and compliance with environmental legislation. All observations, which were recorded on the
inspection checklists, were passed to the Contractor together with the ET’s
recommendations.
9.
As advised
by the Contractor and verified by ET:
·
No
non-compliance regarding the site inspection was received in the reporting
month;
·
Five
environmental complaints were received during the reporting month; and
·
No summons and
prosecution was received in this reporting month.
10.
The major
construction works for the upcoming three months will be:
·
Site
cleaning and tidying at I-1, I-2, I-3 and Outfall;
·
Tree
transplanting at I-1, I-2, I-3 and Outfall;
·
Drilling
rig at I-3 and Outfall;
·
Soil
nailing at I-1, I-3 and Outfall;
·
Breaking up
exiting boulder at I-1, I-2, I-3, and Outfall;
·
Formation
of access road at I-3 and Outfall;
·
Erosion
control mat and green wire mesh at Outfall;
·
Excavation
and Lateral Support (ELS) at I-1;
·
Construction
of skin wall at I-2 and I-3;
·
Formation
of steel platform at I-2
·
Formation
of shaft at I-2; and
·
Launching
chamber at Outfall.
1.1.1
The
Drainage Services Department (DSD) proposed to construct a tunnel with an
internal diameter of 6.5m and a length of 5.13km, with the purpose to alleviate
the flooding risk in Tsuen Wan and Kwai Chung.
1.1.2
This
project is a Designated Project under Schedule 2 Part I Category Q, of the Environmental Impact
Assessment Ordinance (EIAO) as part of the proposed Tsuen Wan Drainage Tunnel
(TWDT) passes underneath the existing Tai Mo Shan Country Park. An Environmental Impact Assessment (EIA) Study
has therefore been undertaken to provide information on the nature and extent
of environmental impacts arising from the construction and operation of the
proposed designed project and related activities taking place
concurrently. From the EIA the
recommendations for monitoring contained herein, are made.
1.1.3
The Maeda-CREC-SELI
Joint Venture (MCSJV) was awarded by DSD with the Contract – Design
and Construction of Tsuen Wan Drainage Tunnel.
1.1.4
Hyder was
commissioned by the MCSJV as the Environmental Team (ET) to implement an
EM&A program in accordance with the EM&A Manual. The proposed tunnel section flows from the
junction of Shing Mun Road and Wo Yi Hop Road and discharges to south of Yau
Kom Tau underneath Castle Peak Road as shown in Appendix A.
1.1.5
The
construction works of the Project was commenced in January 2008. This is the
seventeenth monthly EM&A report summarising the impact monitoring results
and audit findings of the EM&A program in August 2009.
2.1 Project Organization and Management Structure
2.1.1
The
organization chart and lines of communication with respect to the on-site
environmental management are shown in Appendix B.
2.2.1
The overall
project programme from the detail design to completion of all civil works shall
take approximately 54 months. The construction programme is presented in
Appendix C.
2.2.2
The major construction
activities undertaken in the reporting month were:
·
Site
cleaning and tidying at I-1, I-2, I-3 and Outfall;
·
Tree
transplanting at I-1, I-2, I-3 and Outfall;
·
Drilling
rig at I-3 and Outfall;
·
Soil
nailing at I-1, I-3 and Outfall;
·
Breaking up
exiting boulder at I-1, I-2, I-3 and Outfall;
·
Formation
of access road at I-3 and Outfall;
·
Erosion
control mat and green wire mesh at Outfall;
·
Excavation
and Lateral Support (ELS) at I-1;
·
Construction
of skin wall at I-3; and
·
Formation
of steel platform at I-2.
2.2.3
No
construction activities were undertaken for TWDT during the restricted hours.
2.3.1
The
implemented environmental mitigation measures and their statuses are given in
Appendix D.
2.4 Status of License and Permit
2.4.1 A summary of relevant permits and licences for the Project is given in Appendix E.
3.1.1
1-hour Total
Suspended Particulates (TSP) levels are measured at the designated air
monitoring locations in accordance with the EM&A Manual. Information such
as date of monitoring, duration, weather condition, equipment used and
monitoring results were recorded on the field data sheet developed for the
Project. The monitoring results are presented in Section 4.
3.1.2
1-hour TSP
monitoring is carried out under typical weather conditions (with no adverse
weather such as typhoon signal or rain storm warning) three times every six
days using High Volume Air Samplers (HVASs).
Monitoring should be conducted in accordance with the standard sampling
method as set out in High Volume Method for Total Suspended Particulates, Part
50 Chapter 1 Appendix B, Title 40 of the Code of Federal Regulations of the
USEPA.
3.1.3
After each
sampling, the filter paper loaded with dust is kept in a clean and tightly
sealed plastic bag. The filter paper is then re-conditioned in desiccators for
24 hours before obtaining the weight under laboratory conditions.
3.1.4
The average
concentrations of the TSP are calculated based on the following information
obtained from monitoring:
·
Flow rate;
·
Weight of
the filter paper before and after sampling; and
·
Sampling
period indicated by the elapsed-time meter.
3.1.5
All samples
should be kept in good condition (i.e. stored in sealed plastic bags, with
brief description of the monitoring dates and locations) for a period of 6
months before disposal. Sample analysis is carried out by ALS Technichem (HK) Pty Limited (HOKLAS Registration Number
066).
Monitoring Equipment and Calibration
3.1.6
High Volume
Air Samplers (HVASs) are used for 1-hour TSP monitoring to comply with the
USEPA specifications in Appendix B Part 5 - Reference Method for the
Determination of Suspended Particulate matter in the Atmosphere (High-Volume
Method) of the Code of Federal Regulation dated June 1, 1991.
3.1.7
All HVASs
are calibrated before commencement of monitoring using standard orifice
5-points calibration method with orifice calibrator to determine the actual
flow rate of each HVAS. This shall be
used for the calculation of the TSP level.
Calibration Kit Model - TE5025A
is used for calibration of the HVAS.
Recalibration of the HVAS shall be carried out after motor maintenance,
at least once every six months, which is about the expected life of carbon
brush. The air quality monitoring equipment used during the reporting month is
shown in Table
3‑1 below. The
calibration certificates are included in Appendix F.
|
Equipment Type |
Model |
Serial Number |
Calibration Orifice Number |
Location |
|
HVAS |
BM2000HX |
4994 |
1559 |
ASR 1 |
|
HVAS |
BM2000HX |
5875 |
1559 |
ASR 3 |
|
HVAS |
TE5005X |
0390 |
1559 |
ASR 8 |
|
HVAS |
TE5005X |
0646 |
1559 |
ASR 9 |
Table 3‑1 Air Quality Monitoring Equipment
3.1.8
Four
designated air quality-monitoring locations were identified in the contract
specific EM&A manual. They are
listed in Table
3‑2 below and shown in Appendix G.
|
Monitoring
Station ID |
Name of
Premises |
Floor
Level |
|
ASR1 |
|
G/F |
|
ASR3 |
|
Podium |
|
ASR8 |
|
G/F |
|
ASR9 |
Greenview Terrace (Block 1) |
G/F |
Table 3‑2 Air Quality Monitoring Locations
3.1.9
The Action
and Limit Levels for the 1-hour TSP monitoring is shown in Table 3‑3. In case
exceedances of Action and/or Limit levels for air quality occur, Event
Contingency Plans (ECPs) would be implemented.
The ECPs for Action and Limit levels exceedances are shown in Table 3‑4.
|
Station |
1-hr TSP Level in μg/m3 |
|
|
Action Level |
Limit Level |
|
|
ASR 1 |
307 |
500 |
|
ASR 3 |
327 |
500 |
|
ASR 8 |
337 |
500 |
|
ASR 9 |
329 |
500 |
Table 3‑3 Action & Limit Levels for Air Quality
|
EVENT |
ACTION |
|||||||
|
ET |
IEC |
SOR |
CONTRACTOR |
|||||
|
ACTION
LEVEL |
||||||||
|
Exceedance
for one sample |
· Identify source, investigate the causes of exceedance and propose remedial measures; · Inform IEC and SOR; · Repeat measurement to confirm finding; · Increase monitoring frequency to daily. |
· Check monitoring data submitted by ET; · Check Contractor’s working method. |
· Notify Contractor. |
· Rectify any unacceptable practice; · Amend working methods if appropriate. |
||||
|
Exceedance
for two or more consecutive samples |
· Identify source; · Inform IEC and SOR; · Advise SOR on the effectiveness of the proposed remedial measures; · Repeat measurements to confirm findings; · Increase monitoring frequency to daily; · Discuss with IEC and Contractor on remedial actions required; · If exceedance continues, arrange meeting with IEC and SOR; · If exceedance stops, cease additional monitoring. |
· Check monitoring data submitted by ET; · Check Contractor’s working method; · Discuss with ET and Contractor on possible remedial measures; · Advise the ET on the effectiveness of the proposed remedial measures; · Supervise Implementation of remedial measures. |
· Confirm receipt of notification of exceedance in writing; · Notify Contractor; · Ensure remedial measures properly implemented. |
· Submit proposals for remedial to SOR within 3 working days of notification; · Implement the agreed proposals; · Amend proposal if appropriate. |
||||
|
LIMIT
LEVEL |
||||||||
|
Exceedance
for one sample |
· Identify source, investigate the causes of exceedance and propose remedial measures; · Inform IEC, SOR, Contractor and EPD; · Repeat measurement to confirm finding; · Increase monitoring frequency to daily; · Assess effectiveness of Contractor’s remedial actions and keep IEC, EPD and SOR informed of the results. |
· Check monitoring data submitted by ET; · Check Contractor’s working method; · Discuss with ET and Contractor on possible remedial measures; · Advise SOR on the effectiveness of the proposed remedial measures; · Supervise implementation of remedial measures. |
· Confirm receipt of notification of exceedance in writing; · Notify Contractor; · Ensure remedial measures properly implemented. |
· Take immediate action to avoid further exceedance; · Submit proposals for remedial actions to IEC within 3 working days of notification; · Implement the agreed proposals; · Amend proposal if appropriate. |
||||
|
Exceedance
for two or more consecutive samples |
· Notify IEC, SOR, Contractor and EPD; · Identify source; · Repeat measurement to confirm findings; · Increase monitoring frequency to daily; · Carry out analysis of Contractor’s working procedures to determine possible mitigation to be implemented; · Arrange meeting with IEC and SOR to discuss the remedial actions to be taken; · Assess effectiveness of Contractor’s remedial actions and keep IEC, EPD and SOR informed of the results; · If exceedance stops, cease additional monitoring. |
· Discuss amongst SOR, ET, and Contractor on the potential remedial actions; · Review Contractor’s remedial actions whenever necessary to assure their effectiveness and advise SOR accordingly; · Supervise the implementation of remedial measures. |
· Confirm receipt of notification of exceedance in writing; · Notify Contractor; · In consultation with the IEC, agree with the Contractor on the remedial measures to be implemented; · Ensure remedial measures properly implemented; · If exceedance continues, consider what portion of the work is responsible and instruct the Contractor to stop that portion of work until the exceedance is abated. |
· Take immediate action to avoid further exceedance; · Submit proposals for remedial actions to IEC within 3 working days of notification; · Implement the agreed proposals; · Resubmit proposals if problem still not under control; · Stop the relevant portion of works as determined by SOR until the exceedance is abated. |
||||
Table 3‑4 Event/Action Plan for Air Quality
3.2.1
The construction noise level is
measured in terms of equivalent A-weighted sound pressure level (Leq)
measured in decibels (dB(A)). Monitoring
of Leq(30 min) is carried out at the noise monitoring locations on a
weekly basis during normal construction working hours (0700-1900 hours from
Monday to Saturday except public holidays).
For all other time periods (i.e. restricted hours), Leq(5 min)
would be employed for comparison with the Noise Control Ordinance (NCO)
criteria if necessary.
3.2.2
The two statistical sound levels L10
and L90: the level exceeded for 10 and 90 percent of the time
respectively, are also recorded during monitoring. Major noise sources observed, both on-site
and off-site, are recorded on the field data sheet. All measurements are recorded to the nearest
0.1 dB(A) and presented in round numbers in this report. Results are presented in Section 4.
3.2.3
Sound level meters, which comply with
the International Electrotechnical Commission Publication 651: 1979 (Type 1)
and 804: 1985 (Type 1) specifications as referred to the Technical Memorandum
(TM) issued under the Noise Control Ordinance, are used. Noise levels for the A-weighted levels Leq(30min),
L10 and L90 are measured throughout the impact
monitoring. Average, by sound power, of
six consecutive 5 minutes readings is used to provide Leq(30 min) for
non-restricted hours (07:00-19:00 hours from Monday to Saturday except public
holidays). A facade correction of 3dB(A)
is applied to the measurements that are carried out under free field
conditions.
3.2.4
During the impact monitoring,
parameters such as dates, weather condition, equipment used, measurement
results and major noise sources are recorded on the field data record
sheet. Monitoring would not be carried
out in the presence of fog, rain or strong wind with a steady speed exceeding 5
m/s. In relation to the monitored noise
levels, other noise sources such as road traffic might make a significant
contribution to the overall noise environment.
Therefore, noise monitoring activities would take into account such
influencing factors, which were not present during the baseline monitoring
period.
Monitoring Equipment and Calibration
3.2.5
Rion Precision Sound Level Meters of
Type NA-27 and Type NL-18 in compliance with the International Electrotechnical
Commission Publication 651: 1979 (Type 1) and 804: 1985 (Type 1)
Specifications, stated in the Technical Memorandum (TM) issued under the NCO,
are used for noise monitoring in this reporting month.
3.2.6
Prior to and following each noise
measurement, the accuracy of the sound level meters is checked using an
acoustic calibrators (Rion Type NC-73) generating a known sound pressure level
at a known frequency. Measurements are
considered as valid only if the calibration levels from before and after the
noise measurement agrees to within 1.0 dB(A).
The sound level meters and the calibrator are calibrated annually to
ensure they perform to the same level of accuracy as stated in the
manufacturer’s specifications. The noise
monitoring equipment used during the reporting month is shown in Table 3‑5 below. The
calibration certificates are included in Appendix F.
|
Equipment
Type |
Manufacturer |
Type
Number |
Serial
Number |
Location |
|
Sound
Level Meter |
Rion |
NA-27 |
00201194 |
NSR1,
NSR3, NSR6, NSR8 and NSR9 |
|
Sound
Level Meter |
Rion |
NL-18 |
00360030 |
|
|
Sound
Level Calibrator |
Rion |
NC-73 |
10786708 |
|
|
Sound
Level Calibrator |
Rion |
NC-73 |
10997142 |
Table 3‑5 Noise Monitoring Equipment
3.2.7
Five designated noise monitoring
locations were identified in the contract specific EM&A manual. They are listed in Table 3‑6 below and shown in Appendix G. All the locations below are in façade measurement.
|
Monitoring Station ID |
Name of Premises |
Floor Level |
|
NSR1 |
|
G/F |
|
NSR3 |
|
Podium |
|
NSR6 |
Squatters |
G/F |
|
NSR8 |
|
G/F |
|
NSR9 |
Greenview Terrace (Block 1) |
Podium (up to 6 July2009) Roof* (from 16 July 2009) |
* The noise monitoring location of NSR9 had been
adjusted at rooftop from 16 July 2009.
Table 3‑6 Noise Monitoring Locations
Construction Groundborne Noise
3.2.8
Prediction of construction
groundborne noise indicates the criteria will be achieved at most NSRs except
exceedances are predicted at Hong Hoi Chee Hong Temple (NSR3) and Squatters
(NSR6). It is recommended to restrict
the TBM operation in non-restricted period (i.e. 0700 - 1900) at these NSRs. In
order to ensure proper control of groundborne noise is executed by the
contractor, a monitoring requirement is recommended at the
3.2.9
The criteria including Technical
Memorandum for the Assessment of Noise from Places other than Domestic
Premises, Public Places or Construction Sites (TM-Places) under the NCO
stipulates that noise transmitted primarily through the structural elements of
building, or buildings, shall be 10 dB(A) less than the relevant ANLs. Daytime groundborne construction noise
criterion of 60 dB(A) therefore applies with reference to TM-EIAO 70 dB(A)
criterion for schools and taking account of the minus 10 dB(A) requirement
under the NCO TM-Places. Following the
same principle for groundborne noise criteria, groundborne construction noise
levels inside domestic premises relying on opened window for ventilation will
be limited to 65 dB(A), with reference to the daytime airborne noise criterion
of 75 dB(A) in accordance with TM-EIAO.
3.2.10
The Action and Limit levels for
construction noise are defined in Table
3‑7. If non-compliance
of the criteria occurs, actions in accordance with the Action Plan in Table 3‑8 would be carried out.
|
Time Period |
Action |
Limit |
|
0700 – 1900 hrs on normal weekdays |
When one documented complaint is received |
75 dB(A)* |
Table 3‑7 Action
& Limit Levels for Noise
|
Event |
Action |
|||
|
ET Leader |
IEC |
SOR |
Contractor |
|
|
Action Level |
· Notify IEC and the Contractor. · Carry out investigation. · Report the results of investigation to IEC and the Contractor. · Discuss with the Contractor and formulate remedial measures. · Increase monitoring frequency to check mitigation measures. |
· Review with analysed results submitted by ET. · Review the proposed remedial measures by the Contractor and advise SOR accordingly. · Supervise the implement of remedial measures. |
· Confirm receipt of notification of exceedance in writing. · Notify the Contractor. · Require the Contractor to propose remedial measures for the analysed noise problem. · Ensure remedial measures are properly implemented. |
· Submit noise mitigation proposals to IEC. · Implement noise mitigation proposals. |
|
Limit Level |
· Identify the source. · Notify IEC, SOR, EPD and the Contractor. · Repeat measurement to confirm findings. · Increase monitoring frequency. · Carry out analysis of Contractor’s working procedures to determine possible mitigation to be implemented. · Inform IEC, SOR, and EPD the causes & actions taken for the exceedances. · Assess effectiveness of the Contractor’s remedial actions and keep IEC, EPD and SOR informed of the results. · If exceedance stops, cease additional monitoring. |
· Discuss amongst SOR, ET Leader and the Contractor on the potential remedial actions. · Review the Contractor’s remedial actions whenever necessary to assure their effectiveness and advise SOR accordingly. · Supervise the implementation of remedial measures. |
· Confirm receipt of notification of exceedance in writing. · Notify the Contractor. · Require the Contractor to propose remedial measures for the analysed noise problem. · Ensure remedial measures are properly implemented. · If exceedance continues, consider what activity of the work is responsible and instruct the Contractor to stop that activity of work until the exceedance is abated. |
· Take immediate action to avoid further exceedance. · Submit proposals for remedial actions to IEC within 3 working days of notification. · Implement the agreed proposals. · Resubmit proposals if problem still not under control. · Stop the relevant activity of works as determined by the SOR until the exceedance is abated. |
Table 3‑8 Event/Action Plan for Noise
3.3.1
The water
quality impact would be insignificant with the protection measures recommended
in Section 5.6 of the EIA report. However
in view of the sensitive nature of the rivers/streams and bathing beaches in the Study Area, it is suggested that a
programme of monitoring should be established to confirm the mitigation
measures are protecting these water bodies.
3.3.2
Monitoring
for Dissolved Oxygen (DO), temperature, turbidity, pH and suspended solids (SS)
should be undertaken at designated monitoring locations. It should be noted that DO, temperature, turbidity and pH should be
measured in-situ whereas SS is assayed in a laboratory.
3.3.3
In
association with the water quality parameters, other relevant data should also
be measured, such as monitoring location/position, time, weather conditions,
and any special phenomena and description of work underway
at the construction site etc.
3.3.4
In accordance with the EM&A Manual, the water quality monitoring
for all specified parameters shall be measured at all designated monitoring
locations including control points at an interval of 3 days per week. DO,
temperature, turbidity, pH and SS shall be undertaken at designated monitoring
locations.
3.3.5
It should be noted that water samples for all monitoring
parameters should be collected, stored, preserved and analysis according to
Standard Methods, APHA 17 ed. and/or methods agreed by the Director of
Environmental Protection.
3.3.6
Each sample
shall be analysed in accordance with the APHA Standard Methods for the
Examination of Water and Wastewater, 18th edition, or an equivalent method
approved by the EPD. If an in-house or
non-standard method is proposed, details of the method verification may require
to be submitted to the EPD. In any
circumstance, the sample testing should comply with a comprehensive quality
assurance and quality control programme.
The laboratory should be prepared to demonstrate the quality programmes
to the EPD when requested.
Monitoring Equipment and Calibration
3.3.7
All
the water samples collected should be transferred to clearly labelled and pre-cleaned sample containers with necessary
preservatives immediately after collection.
The sample containers should be provided by a HOKLAS accredited
laboratory. Sufficient quantity of
samples should be collected for all laboratory analyses. Following sampling, samples should be stored in a cool box at temperature of between 0 and
4oC, and transported to the laboratory within the sample retention
time as advised by the laboratory under proper chain-of-custody system. The water
quality monitoring equipment used during the reporting month is shown in Table 3‑9 below.
|
Equipment Type |
Manufacturer |
Model |
Quantity |
|
pH Meter / DO / Temperature Meter |
WTW |
PH/Oxi 340i |
1 |
|
Tuibidimeter |
EUTECH |
TN-100 |
1 |
Table 3‑9 Water Quality Monitoring Equipment
3.3.8
All pH
meters, DO meters and turbidimeters shall be checked and calibrated prior to
use. DO meters and turbidimeters shall
be calibrated by a laboratory accredited under HOKLAS or any other
international accreditation scheme, and subsequently re-calibrated at 3 monthly
intervals throughout all stages of the water quality monitoring. Responses of sensors and electrodes shall be
checked with certified standard solutions before each use. Wet bulb calibrations for all DO meters shall
be carried out before measurement at each monitoring location. For the on site calibration of field
equipment, BS 127:1993, "Guide to field and on-site test methods for the
analysis of waters" should be observed.
The calibration certificates are included in Appendix
F.
3.3.9
Four designated
monitoring locations were identified in the contract specific EM&A Manual for water
quality monitoring. While the construction of the outfall basin at the
seashore has not been started, monitoring of marine water quality is only
required during which the rip rap is placed at the seashore area. These
four monitoring stations are listed in Table 3‑10 below and
shown in Appendix G.
|
Monitoring Station ID |
Name of Premises |
|
I-1 |
Intake I-1 |
|
I-1-C |
Control of Intake I-1 |
|
I-2 |
Intake I-2 |
|
I-2-C |
Control of Intake I-2 |
|
I-3 |
Intake I-3 |
|
I-3-C* |
Control of Intake I-3 |
|
O-1 (FT) |
Outfall 1During Flood Tide |
|
O-1 (ET) |
Outfall 1During Ebb Tide |
|
O-1-C (FT) |
Control of Outfall O-1 During Flood Tide |
|
O-1-C (ET) |
Control of Outfall O-1 During Ebb Tide |
Table 3‑10 Water Quality Monitoring Locations
3.3.10
Note that there are two control stations for Outfall O-1, one for
sampling during flood tide and one for sampling during ebb tide. Only one of those control stations for
Outfall O-1 shall be sampled during each sampling. Control station to be sampled will be
determined based on the tidal information provided by the Hong Kong
Observatory.
3.3.11
The Action and Limit levels for water
quality monitoring parameters are defined in Table 3‑11. In case
of any exceedance, appropriate actions will be undertaken in accordance with
the Event and Action Plan as described in Table
3‑12.
|
Parameters |
Action |
Limit |
|
DO in
mg/l (Surface,
Middle & Bottom) |
Surface
& Middle 5%-ile
of baseline data for surface and middle layer. Bottom 5%-ile
of baseline data for bottom layer. |
Surface
& Middle 4mg/l
except 5mg/l for FCZ or 1%-ile
of baseline data for surface and middle layer Bottom 2mg/l
or 1%-ile of baseline data for bottom layer |
|
SS in
mg/l (depth-averaged) |
95%-ile
of baseline data or 120% of upstream control station’s SS at the same tide of
the same day |
99%-ile
of baseline or 130% of upstream control station’s SS at the same tide of the
same day and specific sensitive receiver water quality requirements (e.g.
required suspended solids levels for concerned sea water intakes) |
|
Turbidity
(Tby) in NTU (depth-averaged) |
95%-ile
of baseline data or 120% of upstream control station’s Tby at the same tide
of the same day |
99%-ile
of baseline or 130% of upstream control station’s Tby at the same tide of the
same day |
Notes:
·
For DO,
non-compliance of the water quality limits occurs when monitoring result is
lower than the limits.
·
For SS and
Tby, non-compliance of the water quality limits occurs when monitoring result
is higher than the limits.
·
All the
figures given in the table are used for reference only and the EPD may amend
the figures whenever it is considered as necessary.
Table 3‑11 Action/Limit Levels for Water Quality
|
Event |
ET Leader |
IEC |
SOR |
Contractor |
|
Action Level being exceeded by one sampling day |
· Repeat in-situ measurement to confirm finding; · Identify source(s) of impact; · Inform IEC and Contractor; · Check monitoring data, all plant, equipment and Contractor’s working methods; · Discuss mitigation measures with IEC and Contractor; and · Repeat measurement on next day of exceedance. |
· Discuss with ET and Contractor on the mitigation measures; · Review proposals on mitigation measures submitted by Contractor and advise the SOR accordingly; and · Assess the effectiveness of the implemented mitigation measures. |
· Discuss with IEC on the proposed mitigation measures; and · Make agreement on the mitigation measures to be implemented. |
· Inform the SOR and confirm notification of the non-compliance in writing; · Rectify unacceptable practice; · Check all plant and equipment; · Consider changes of working methods; · Discuss with ET and IEC and propose mitigation measures to IEC and SOR; and · Implement the agreed mitigation measures. |
|
Action Level being exceeded by more than one consecutive sampling day |
· Repeat in-situ measurement to confirm finding; · Identify source(s) of impact; · Inform IEC and Contractor; · Check monitoring data, all plant, equipment and Contractor’s working methods; · Discuss mitigation measures with IEC and Contractor; · Ensure mitigation measures are implemented; · Prepare to increase the monitoring frequency to daily; and · Repeat measurement on next day of exceedance. |
· Discuss with ET and Contractor on the mitigation measures; · Review proposals on mitigation measures submitted by Contractor and advise the SOR accordingly; and · Assess the effectiveness of the implemented mitigation measures. |
· Discuss with IEC on the proposed mitigation measures; · Make agreement on the mitigation measures to be implemented; and · Assess the effectiveness of the implemented mitigation measures. |
· Inform the Engineer and confirm notification of the non-compliance in writing; · Rectify unacceptable practice; · Check all plant and equipment; · Consider changes of working methods; · Discuss with ET and IEC and propose mitigation measures to IEC and SOR within 3 working days; and · Implement the agreed mitigation measures. |
|
Limit Level being exceeded by one sampling day |
· Repeat in-situ measurement to confirm finding; · Identify source(s) of impact; · Inform IEC, Contractor and EPD; · Check monitoring data, all plant, equipment and Contractor’s working methods; · Discuss mitigation measures with IEC, SOR and Contractor; · Ensure mitigation measures are implemented; and · Increase the monitoring frequency to daily until no exceedance of Limit level. |
· Discuss with ET and Contractor on the mitigation measures; · Review proposals on mitigation measures submitted by Contractor and advise the SOR accordingly; and · Assess the effectiveness of the implemented mitigation measures.
|
· Discuss with IEC, ET and Contractor on the proposed mitigation measures; and · Request Contractor to critically review the working methods; · Make agreement on the mitigation measures to be implemented; and · Assess the effectiveness of the implemented mitigation measures. |
· Inform the Engineer and confirm notification of the non-compliance in writing; · Rectify unacceptable practice; · Check all plant and equipment; · Consider changes of working methods; · Discuss with ET and IEC and SOR and propose mitigation measures to IEC and SOR within 3 working days; and · Implement the agreed mitigation measures. |
|
Limit Level being exceeded by more than one consecutive sampling day |
· Repeat in-situ measurement to confirm finding; · Identify source(s) of impact; · Inform IEC, Contractor and EPD; · Check monitoring data, all plant, equipment and Contractor’s working methods; · Discuss mitigation measures with IEC, SOR and Contractor; · Ensure mitigation measures are implemented; and · 7. Increase the monitoring frequency to daily until no exceedance of Limit level for two consecutive days. |
· Discuss with ET and Contractor on the mitigation measures; · Review proposals on mitigation measures submitted by Contractor and advise the SOR accordingly; and · Assess the effectiveness of the implemented mitigation measures. |
· Discuss with IEC, ET and Contractor on the proposed mitigation measures; and · Request Contractor to critically review the working methods; · Make agreement on the mitigation measures to be implemented; · Assess the effectiveness of the implemented mitigation measures; and · Consider and instruct, if necessary, the Contractor to slow down or to stop all or part of the marine work until no exceedance of Limit Level. |
· Inform the SOR and confirm notification of the non-compliance in writing; · Rectify unacceptable practice; · Check all plant and equipment; · Consider changes of working methods; · Discuss with ET and IEC and SOR and propose mitigation measures to IEC and SOR within 3 working days; · Implement the agreed mitigation measures; and · As directed by the Engineer, to slow down or to stop all or part of the marine work or construction activities. |
Table 3‑12 Event/Action Plan for Water Quality
4.1.1
The air
quality monitoring schedule of the reporting period is given in Appendix
H.
4.1.2
Results of 1-hours TSP level are shown
in Table 4-1. All
measurements were recorded to the nearest 0.1mg/m3
and presented in round numbers in this report.
Detail results including weather conditions, and graphical presentations
are presented in Appendix I.
|
Station |
Monitoring Date |
Monitoring Result (mg/m3) |
Action/Limit Levels (mg/m3) |
|
ASR 1 |
03-Jul-09 |
126.4 |
307/500 |
|
111.6 |
|||
|
80.8 |
|||
|
07-Aug-09 |
100.7 |
||
|
109.2 |
|||
|
121.5 |
|||
|
13-Aug-09 |
99.4 |
||
|
87.1 |
|||
|
92.1 |
|||
|
19-Aug-09 |
43.0 |
||
|
36.8 |
|||
|
60.1 |
|||
|
25-Aug-09 |
95.7 |
||
|
56.5 |
|||
|
46.6 |
|||
|
31-Aug-09 |
94.5 |
||
|
139.9 |
|||
|
116.6 |
|||
|
ASR 3 |
03-Jul-09 |
165.7 |
327/500 |
|
82.8 |
|||
|
85.1 |
|||
|
07-Aug-09 |
187.4 |
||
|
83.8 |
|||
|
156.5 |
|||
|
13-Aug-09 |
187.4 |
||
|
84.9 |
|||
|
75.0 |
|||
|
19-Aug-09 |
78.3 |
||
|
46.3 |
|||
|
57.3 |
|||
|
25-Aug-09 |
115.8 |
||
|
48.5 |
|||
|
40.8 |
|||
|
31-Aug-09 |
81.6 |
||
|
126.8 |
|||
|
94.8 |
|||
|
ASR 8 |
03-Jul-09 |
129.4 |
337/500 |
|
134.6 |
|||
|
124.2 |
|||
|
07-Aug-09 |
101.2 |
||
|
103.9 |
|||
|
152.4 |
|||
|
13-Aug-09 |
138.9 |
||
|
98.5 |
|||
|
107.9 |
|||
|
19-Aug-09 |
98.5 |
||
|
79.6 |
|||
|
87.7 |
|||
|
25-Aug-09 |
107.9 |
||
|
90.4 |
|||
|
60.7 |
|||
|
31-Aug-09 |
89.0 |
||
|
116.0 |
|||
|
105.2 |
|||
|
ASR 9 |
03-Jul-09 |
173.5 |
329/500 |
|
104.5 |
|||
|
105.6 |
|||
|
07-Aug-09 |
116.8 |
||
|
90.2 |
|||
|
168.9 |
|||
|
13-Aug-09 |
239.5 |
||
|
100.6 |
|||
|
72.9 |
|||
|
19-Aug-09 |
118.0 |
||
|
77.5 |
|||
|
99.5 |
|||
|
25-Aug-09 |
121.5 |
||
|
49.7 |
|||
|
64.8 |
|||
|
31-Aug-09 |
84.5 |
||
|
218.6 |
|||
|
87.9 |
Note: Italic indicates the occurrence of exceedance of
Action level
Bold indicates the occurrence of
exceedance of Limit Level
Table 4-1 Air
Quality Monitoring Results
4.1.3
No project related exceedance was
recorded in the reporting month.
4.2.1
The noise monitoring schedule of the
reporting period is given in Appendix H.
Results of measured noise level, in terms of Leq (30min), during the
construction are shown in Table 4-2. All measurements including L10 and L90 are recorded
to the nearest 0.1 dB(A) and presented in round numbers in this report. Detail results including weather conditions
and graphical presentation are presented in Appendix I.
|
Station |
Monitoring Date |
Leq (30 min) dB(A) |
Limit Levels dB(A) |
|
NSR 1 |
03-Aug-09 |
68.2** |
70 |
|
14-Aug-09 |
70.3 |
||
|
19-Aug-09 |
66.3 |
||
|
25-Aug-09 |
69.4 |
||
|
31-Aug-09 |
64.1 |
||
|
NSR 3 |
03-Aug-09 |
67.5 |
75 |
|
14-Aug-09 |
71.1 |
||
|
19-Aug-09 |
70.4 |
||
|
25-Aug-09 |
72.5 |
||
|
31-Aug-09 |
72.4 |
||
|
NSR 6 |
03-Aug-09 |
57.1 |
|
|
14-Aug-09 |
55.8 |
||
|
19-Aug-09 |
55.7 |
||
|
25-Aug-09 |
56.0 |
||
|
31-Aug-09 |
58.9 |
||
|
NSR 8 |
03-Aug-09 |
68.0 |
|
|
14-Aug-09 |
65.0 |
||
|
19-Aug-09 |
68.9 |
||
|
25-Aug-09 |
66.3 |
||
|
28-Aug-09* |
66.4 |
||
|
31-Aug-09 |
67.8 |
||
|
NSR 9 |
03-Aug-09 |
72.3 |
|
|
10-Aug-09* |
73.0 |
||
|
12-Aug-09* |
74.1 |
||
|
14-Aug-09 |
72.6 |
||
|
15-Aug-09* |
71.5 |
||
|
17-Aug-09* |
70.9 |
||
|
19-Aug-09 |
72.1 |
||
|
25-Aug-09 |
73.0 |
||
|
28-Aug-09* |
73.5 |
||
|
31-Aug-09 |
73.5 |
* Additional noise monitoring. ** Corrected Noise Level (CNL)
Table 4-2 Noise Monitoring Results
4.2.2
No exceedances of Limit Level were
recorded during the reporting month. However, five complaints were received on
29 July, 11, 12, 14 and 17 August 2009 regarding the daytime construction noise
at NSR 8 and NSR 9. Hence, they would be Action Level exceedances. Details of
the complaints are presented in Section 7 and the notification of exceedances
is enclosed in Appendix J.
4.3.1
The water quality monitoring schedule
of the reporting period is given in Appendix H.
Summaries of exceedances for water quality monitoring are provided in Table 4-3 to Table 4-5.
|
Parameter |
Action Level
Exceedance |
Limit
Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
One
recorded on 28 August |
One
recorded on 14 August |
|
Total |
One |
One |
Table 4-3 Summary of Exceedances for I-1
|
Parameter |
Action
Level Exceedance |
Limit
Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
Nil |
One
recorded 14 August |
|
Total |
Nil |
One |
Table 4-4 Summary of Exceedances for I-2
|
Parameter |
Action Level
Exceedance |
Limit
Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
Nil |
Nil |
|
Total |
Nil |
Nil |
Table 4-5 Summary of Exceedances for I-3
4.3.2
Results
of measured water quality parameters during the reporting month are shown in Table 4-6 and detailed results including weather conditions and
graphical presentations are enclosed in Appendix I.
4.3.3
No water quality monitoring was done on 12 August 2009 due to
thunderstorm warning.
4.3.4
The
exceedance of Control Limit Level of SS (130% higher than I-1-C) recorded at
I-1 on 14 August 2009 was below
baseline Action / Limit Level and was within the range of baseline SS concentration.
Site
cleanliness and tidiness, excavation and breaking up of rock strata, and
disposal of C&D materials were carried out during the measurements. No
direct disturbance was observed from the site. The exceedance was considered to
be contributed by natural variation and no action was therefore required.
4.3.5
The exceedance of Control Action Level of SS (120% higher than I-1-C) recorded at I-1 on 28
August 2009 was below baseline
Action / Limit Level and was within the range of baseline SS concentration. Site
cleaning & tidying and shortcreting to the shaft wall were undertaken
during the measurement. The exceedance was considered to
be contributed by natural variation and no action was therefore required.
4.3.6
The exceedance of Control Limit
Level of SS (130% higher than I-2-C) recorded at I-2 on 14 August 2009 was below baseline Action / Limit Level and was
within the range of baseline SS concentration. Site tidiness & cleanliness, erection of
working platform and trimming off cement grout of H-pile as well as grout hole
drilling were undertaken during the measurements. No direct disturbance was
observed from the site. The exceedance was considered to be contributed by
natural variation and no action was therefore required.
4.3.7
The
above mentioned exceedances were considered as non project related, however,
proper mitigation measures had been implemented during measurements. Details of
the above mentioned investigations could be referred to the notifications of
exceedances as enclosed in Appendix J, which have been provided to the IEC for
review.
|
Station |
Date |
Temperature |
DO
(mg/L) |
Action/Limit
Level for DO (mg/L) |
pH |
Turbidity
(NTU) |
Action/Limit
Level for Turbidity (NTU) |
SS
(mg/L) |
Action/Limit
Level for SS (mg/L) |
|
I-1 |
03-Aug-09 |
28.55 |
5.63 |
3.42 / 3.34 |
7.41 |
2.94 |
9.75 / 12.47 |
2.0 |
8.85 / 10.17 |
|
|
05-Aug-09 |
26.50 |
5.17 |
|
7.00 |
4.51 |
|
2.0 |
|
|
|
07-Aug-09 |
28.35 |
6.02 |
|
7.03 |
3.58 |
|
2.0 |
|
|
|
10-Aug-09 |
28.50 |
5.47 |
|
7.13 |
2.99 |
|
2.0 |
|
|
|
12-Aug-09 |
- |
- |
|
- |
- |
|
- |
|
|
|
14-Aug-09 |
28.05 |
5.03 |
|
7.72 |
7.47 |
|
3.7 |
|
|
|
17-Aug-09 |
29.00 |
6.06 |
|
7.07 |
2.48 |
|
2.0 |
|
|
|
19-Aug-09 |
28.80 |
5.49 |
|
7.37 |
2.55 |
|
2.0 |
|
|
|
21-Aug-09 |
27.70 |
5.77 |
|
6.91 |
2.07 |
|
2.0 |
|
|
|
24-Aug-09 |
28.20 |
5.73 |
|
5.48 |
2.17 |
|
2.1 |
|
|
|
26-Aug-09 |
28.05 |
5.17 |
|
6.90 |
3.02 |
|
2.4 |
|
|
|
28-Aug-09 |
28.55 |
4.77 |
|
7.44 |
2.74 |
|
3.35 |
|
|
|
31-Aug-09 |
28.05 |
5.36 |
|
7.45 |
2.64 |
|
2.1 |
|
|
Station |
Date |
Temperature |
DO
(mg/L) |
Action/Limit
Level for DO (mg/L) |
pH |
Turbidity
(NTU) |
Action/Limit
Level for Turbidity (NTU) |
SS
(mg/L) |
Action/Limit
Level for SS (mg/L) |
|
I-1-C |
03-Aug-09 |
28.75 |
6.25 |
- / - |
7.37 |
3.15 |
- / - |
2.0 |
- / - |
|
|
05-Aug-09 |
26.80 |
5.57 |
|
7.03 |
4.60 |
|
2.0 |
|
|
|
07-Aug-09 |
28.50 |
6.19 |
|
6.99 |
3.57 |
|
2.0 |
|
|
|
10-Aug-09 |
28.60 |
5.86 |
|
7.11 |
3.18 |
|
2.0 |
|
|
|
12-Aug-09 |
- |
- |
|
- |
- |
|
- |
|
|
|
14-Aug-09 |
27.95 |
5.55 |
|
7.86 |
7.63 |
|
2.6 |
|
|
|
17-Aug-09 |
28.80 |
6.58 |
|
7.11 |
2.73 |
|
2.0 |
|
|
|
19-Aug-09 |
28.60 |
5.07 |
|
7.40 |
2.36 |
|
2.0 |
|
|
|
21-Aug-09 |
27.45 |
5.85 |
|
7.00 |
2.27 |
|
2.0 |
|
|
|
24-Aug-09 |
28.00 |
5.25 |
|
5.46 |
2.25 |
|
2.4 |
|
|
|
26-Aug-09 |
28.00 |
5.41 |
|
6.93 |
3.17 |
|
2.4 |
|
|
|
28-Aug-09 |
28.70 |
4.22 |
|
7.44 |
3.00 |
|
2.6 |
|
|
|
31-Aug-09 |
27.85 |
5.27 |
|
7.41 |
2.78 |
|
2.3 |
|
|
Station |
Date |
Temperature |
DO
(mg/L) |
Action/Limit
Level for DO (mg/L) |
pH |
Turbidity
(NTU) |
Action/Limit
Level for Turbidity (NTU) |
SS
(mg/L) |
Action/Limit
Level for SS (mg/L) |
|
I-2 |
03-Aug-09 |
28.80 |
5.46 |
3.66 / 3.63 |
7.56 |
2.59 |
6.63 / 6.99 |
2.0 |
7.68 / 8.34 |
|
|
05-Aug-09 |
26.35 |
5.07 |
|
7.07 |
2.97 |
|
2.0 |
|
|
|
07-Aug-09 |
28.80 |
5.72 |
|
7.06 |
2.07 |
|
2.0 |
|
|
|
10-Aug-09 |
28.00 |
5.73 |
|
7.19 |
2.37 |
|
2.0 |
|
|
|
12-Aug-09 |
- |
- |
|
- |
- |
|
- |
|
|
|
14-Aug-09 |
27.50 |
5.19 |
|
7.40 |
4.82 |
|
3.3 |
|
|
|
17-Aug-09 |
28.50 |
5.57 |
|
7.41 |
2.05 |
|
2.0 |
|
|
|
19-Aug-09 |
28.60 |
5.18 |
|
7.19 |
2.60 |
|
2.0 |
|
|
|
21-Aug-09 |
27.55 |
5.07 |
|
6.07 |
2.12 |
|
2.0 |
|
|
|
24-Aug-09 |
28.00 |
4.80 |
|
5.60 |
2.25 |
|
2.0 |
|
|
|
26-Aug-09 |
27.80 |
4.85 |
|
7.31 |
2.65 |
|
2.0 |
|
|
|
28-Aug-09 |
28.00 |
4.78 |
|
7.52 |
2.09 |
|
2.2 |
|
|
|
31-Aug-09 |
28.00 |
4.54 |
|
7.38 |
1.04 |
|
2.0 |
|
|
Station |
Date |
Temperature |
DO
(mg/L) |
Action/Limit
Level for DO (mg/L) |
pH |
Turbidity
(NTU) |
Action/Limit
Level for Turbidity (NTU) |
SS (mg/L) |
Action/Limit
Level for SS (mg/L) |
|
I-2-C |
03-Aug-09 |
28.40 |
6.44 |
- / - |
7.55 |
2.46 |
- / - |
2.0 |
- / - |
|
|
05-Aug-09 |
26.30 |
5.20 |
|
7.12 |
3.06 |
|
2.0 |
|
|
|
07-Aug-09 |
28.10 |
5.74 |
|
7.04 |
2.18 |
|
2.0 |
|
|
|
10-Aug-09 |
27.75 |
5.25 |
|
7.23 |
2.48 |
|
2.0 |
|
|
|
12-Aug-09 |
- |
- |
|
- |
- |
|
- |
|
|
|
14-Aug-09 |
27.60 |
5.27 |
|
7.43 |
5.09 |
|
2.3 |
|
|
|
17-Aug-09 |
28.10 |
6.12 |
|
7.38 |
2.14 |
|
2.0 |
|
|
|
19-Aug-09 |
28.40 |
4.84 |
|
7.22 |
2.52 |
|
2.0 |
|
|
|
21-Aug-09 |
27.00 |
5.59 |
|
6.00 |
2.05 |
|
2.0 |
|
|
|
24-Aug-09 |
27.90 |
5.02 |
|
5.51 |
2.38 |
|
2.0 |
|
|
|
26-Aug-09 |
27.65 |
5.57 |
|
7.31 |
2.76 |
|
2.0 |
|
|
|
28-Aug-09 |
28.00 |
4.65 |
|
7.54 |
2.25 |
|
2.0 |
|
|
|
31-Aug-09 |
27.70 |
4.68 |
|
7.40 |
1.15 |
|
2.0 |
|
|
Station |
Date |
Temperature |
DO
(mg/L) |
Action/Limit
Level for DO (mg/L) |
pH |
Turbidity
(NTU) |
Action/Limit
Level for Turbidity (NTU) |
SS (mg/L) |
Action/Limit
Level for SS (mg/L) |
|
I-3 |
03-Aug-09 |
28.20 |
6.01 |
3.65 / 3.51 |
7.32 |
2.39 |
3.99 / 4.18 |
2.0 |
6.13 / 7.23 |
|
|
05-Aug-09 |
26.10 |
5.31 |
|
7.08 |
3.84 |
|
2.0 |
|
|
|
07-Aug-09 |
28.35 |
5.95 |
|
7.21 |
3.12 |
|
2.0 |
|
|
|
10-Aug-09 |
28.45 |
5.10 |
|
7.06 |
2.52 |
|
2.0 |
|
|
|
12-Aug-09 |
- |
- |
|
- |
- |
|
- |
|
|
|
14-Aug-09 |
27.60 |
5.60 |
|
7.43 |
3.52 |
|
2.0 |
|
|
|
17-Aug-09 |
28.70 |
5.97 |
|
7.48 |
2.47 |
|
2.0 |
|
|
|
19-Aug-09 |
28.50 |
5.03 |
|
7.48 |
2.83 |
|
2.0 |
|
|
|
21-Aug-09 |
27.50 |
5.57 |
|
5.71 |
2.50 |
|
2.0 |
|
|
|
24-Aug-09 |
28.20 |
4.83 |
|
5.48 |
2.90 |
|
2.0 |
|
|
|
26-Aug-09 |
28.10 |
5.24 |
|
7.20 |
2.68 |
|
2.0 |
|
|
|
28-Aug-09 |
27.80 |
4.67 |
|
7.66 |
2.40 |
|
2.0 |
|
|
|
31-Aug-09 |
27.60 |
5.03 |
|
7.58 |
1.78 |
|
2.0 |
|
|
Station |
Date |
Temperature |
DO
(mg/L) |
Action/Limit
Level for DO (mg/L) |
pH |
Turbidity
(NTU) |
Action/Limit
Level for Turbidity (NTU) |
SS
(mg/L) |
Action/Limit
Level for SS (mg/L) |
|
I-3-C |
03-Aug-09 |
28.30 |
6.16 |
- / - |
7.41 |
2.42 |
- / - |
2.0 |
- / - |
|
|
05-Aug-09 |
26.00 |
5.39 |
|
7.11 |
3.95 |
|
2.0 |
|
|
|
07-Aug-09 |
28.45 |
6.07 |
|
7.18 |
3.09 |
|
2.0 |
|
|
|
10-Aug-09 |
28.10 |
5.22 |
|
7.01 |
2.74 |
|
2.0 |
|
|
|
12-Aug-09 |
- |
- |
|
- |
- |
|
- |
|
|
|
14-Aug-09 |
27.50 |
5.83 |
|
7.50 |
3.60 |
|
2.0 |
|
|
|
17-Aug-09 |
28.30 |
5.31 |
|
7.50 |
2.70 |
|
2.0 |
|
|
|
19-Aug-09 |
28.25 |
5.33 |
|
7.50 |
2.86 |
|
2.4 |
|
|
|
21-Aug-09 |
27.70 |
5.58 |
|
5.62 |
2.11 |
|
2.0 |
|
|
|
24-Aug-09 |
28.10 |
5.18 |
|
5.43 |
2.49 |
|
2.0 |
|
|
|
26-Aug-09 |
27.85 |
5.19 |
|
7.19 |
2.75 |
|
2.0 |
|
|
|
28-Aug-09 |
27.45 |
4.99 |
|
7.65 |
2.51 |
|
2.0 |
|
|
|
31-Aug-09 |
27.40 |
4.80 |
|
7.56 |
1.82 |
|
2.4 |
|
Note: Italic indicates the occurrence of exceedance of Action
level.
Bold
indicates the occurrence of exceedance of Limit level.
Table 4-6 Water Quality Monitoring Results
4.4 Summary of Project-Related Exceedances
4.4.1
Table 4-7
summarises the project-related exceedance results recorded in August 2009. Note
that exceedances that are considered not related to the construction activities
are not included in this table.
|
Environmental Monitoring |
Total No. of Measurement |
Action Level
Exceedance |
% of Action Level
Exceedance |
Limit Level
Exceedance |
% of Limit Level
Exceedance |
|
Air Quality |
72 |
0 |
0 |
0 |
0 |
|
Noise |
31 |
5
(Complaints) |
20 |
0 |
0 |
|
Water |
72 |
0 |
0 |
0 |
0 |
Table 4-7 Summary of Project-Related Exceedances
5.1.1
The status of waste management is
summarized in Table 5-1 below.
|
Status of waste management |
Quantity |
|
Inert C&D Material Disposed of to Public Fill at Tuen Mun (m3) |
6,403.3 |
|
Inert C&D Material Reused in other Contracts* (m3) |
2,695.0 |
|
Metals Generated (kg) |
Nil |
|
Paper / Cardboard Packaging (kg) |
Nil |
|
Plastics (kg) |
Nil |
|
Chemical Waste (kg) |
Nil |
|
General Waste Disposed of to NENT Landfill (m3) |
11.7 |
* Other Contracts include CV/2006/01, DC/2007/08, DC/2007/17, DC/2007/06, Ocean Park, DC/2008/12 and HY/2007/09.
Table
5-1 Waste
Generated in August 2009
6 NON-COMPLIANCE AND DEFICIENCY
6.1.1
ET has carried out two site
inspections in the reporting month. All
observations together with the appropriate recommended mitigation measures
where necessary were recorded in the audit checklists that were passed to the
Contractor. Major environmental
deficiencies observed during site inspection/audits and recommendation, which
were made by the ET, are summarised in Table 6-1 below. No
non-compliance was observed.
|
Inspection Date |
Observation |
Recommendation |
Status |
|
Follow-up |
Nil |
Nil |
Nil |
|
6 August 2009 |
1.
Movable noise barrier was observed not close to the
rock breaker at Outfall. 2.
Black smoke emission from the rock breaker was
observed at Outfall. 3.
Water-filled barrier without cap was observed at I-3
4.
Open slope areas at I-3 were observed not covering
with tarpaulin. |
1.
The
Contractor was reminded to place the movable noise barrier as closer as to
the rock breaker. 2.
The Contractor was reminded to provide proper
maintenance to the rock breaker in order to reduce the black smoke emission. 3.
The Contractor was reminded to place the cap for the
water-filled barrier to avoid mosquito breeding. 4.
The Contractor was reminded to cover the open slope
areas at I-3 with tarpaulin. |
1.
During the site inspection on 28 August 09, the movable
noise barrier was placed closed to the rock breaker. (Closed) This item should be continuously inspected
in the coming month as occasional complaints received that the noise barrier
sometimes not closed enough. 2.
During site inspection on 28 August 09, proper
maintenance was provided to the rock breaker and no black smoke was emitted.
(Closed) 3.
During site inspection on 28 August 2009, the cap
was placed for the water-filled barrier. (Closed) 4.
During site inspection on 28 August 2009, the open
slope areas at I-3 were covered with tarpaulin. (Closed) |
|
28 August 2009 |
1.
The site was observed to be dirty and untidy at I-1.
|
1.
The Contractor was reminded to maintain site
cleanliness and tidiness regularly. |
1.
During site inspection on 3 September 2009, site
cleanliness and tidiness were maintained. (Closed) |
Table 6-1 Site Inspection by ET
7.1.1
A complaint
hotline at 9850
3241 of the Contractor has been established for the Project.
7.1.2
Five complaints were received during
the reporting month.
7.1.3
Two
environmental complaints were received by SOR on 29 July and 11 August 2009
regarding daytime construction noise exceedances recorded at Greenview Terrace
(NSR9) on 8, 22, 23, 27 and 29 July 2009 and a large amount dust generated at
the outfall construction site. Two other environmental complaints from
Greenview Terrace were received by SOR via Apple Daily on 12 August 2009 and by
EPD on 14 August 2009. These complaints also referred to the daytime
construction noise level exceedances and construction dust generated at the
outfall construction site. The
Contractor and the environmental team had carried out site investigation and also
joint meeting on 18 August 2009 in response to these recurrent complaints
received from Greenview Terrace. In accordance with the 1-hr TSP monitoring
from July to August 2009, all 1-hr TSP concentrations at ASR9 were below the
established Action and Limit Levels and no exceedance of 1-hr TSP was recorded
during this period. However, the dust complaint on 22 July 2009 was found due
to the soil nailing works. The Contractor was recommended to enhance water spraying continuously
especially in rock breaking activities and soil nailing works. According to the regular noise monitoring
from July to August 2009, all measured noise levels were below the Limit
Levels. Additional noise measurements taken on 10, 12, 15, 17 and 28 August
2009 (refers to Table 4-2) also reviewed the measured noise levels were
complied with the limit level in accordance with the EIAO-TM. However, the
documented complaints for noise were considered to trigger the action level and
the Contractor was reminded to enhance the on-site noise mitigation measures,
such as tools box talk for Contractor’s Team would be carried out for reminding
that the movable barrier should be placed to the breaking activities as much as
possible, three movable noise barriers had been placed on site and the movable
noise barriers would be modified, a joint filler wall would be installed at the
vertical face of westbound to mitigate the noise rebound from the vertical face
to high level of Greenview Terrace and noise monitoring frequency would be
proposed to increase twice per week. Noise monitoring measurement
would be carried out twice per week until all the above mitigation measures
have been implemented on site in order to check the effectiveness of the
mitigation measures. The investigation
reports had been submitted on 31 August 2009.
The implementation of all the above-mentioned noise mitigations was
still in progress and nearly to be completed during the end of the reporting
period. Follow up action
for this complaint would be required in the following month. Detail of the complaint
investigation can be referred to Appendix K.
7.1.4
The fifth
environmental complaint from
7.1.5
Cumulative statistics of
environmental complaints are shown in Table 7-1.
|
Complaints Received in the Reporting Month |
Cumulative Number of Complaints |
|
5 |
9 |
Table
7-1 Cumulative Statistic of Environmental Complaint
8 SUMMARY OF NOTIFICATION OF SUMMONS, SUCCESSFUL PROSECUTIONS AND CORRECTIVE ACTIONS
8.1.1
No summons and successful prosecution was received during the
reporting month.
8.1.2
Cumulative
statistics of Notification of Summons, Successful Prosecutions and Convictions
are shown in Table 8-1.
|
Notification of Summons |
Successful Prosecution |
||
|
August 09 |
Cumulative |
August 09 |
Cumulative |
|
0 |
0 |
0 |
0 |
Table 8-1 Cumulative Statistics of Notification of Summons
and Successful Prosecutions
9.1.1
The forecast of construction works
for the upcoming three months are:
·
Site
cleaning and tidying at I-1, I-2, I-3 and Outfall;
·
Tree
transplanting at I-1, I-2, I-3 and Outfall;
·
Drilling
rig at I-3 and Outfall;
·
Soil
nailing at I-1, I-3 and Outfall;
·
Breaking up
exiting boulder at I-1, I-2, I-3, and Outfall;
·
Formation
of access road at I-3 and Outfall;
·
Erosion
control mat and green wire mesh at Outfall;
·
Excavation
and lateral support (ELS) at I-1;
·
Construction
of skin wall at I-2 and I-3;
·
Formation
of steel platform at I-2;
· Formation of shaft at I-2; and
· Launching chamber at Outfall.
|
|
|
|
|
Site Map and Works Area |
|
|
|
|
|
Organization Chart |
|
|
|
|
|
Construction Programme |
|
|
|
|
|
Implementation Status of Environmental Mitigation Measures |
|
|
|
|
|
Status of License and Permit |
|
|
|
|
|
Calibration Certificates |
|
|
|
|
|
Monitoring Locations |
|
|
|
|
|
EM&A Schedule |
|
|
|
|
|
Monitoring Results |
|
|
|
|
|
Interim Notifications of Environmental Quality Limits Exceedances |
|
|
|
|
|
Complaint Log |