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EXECUTIVE SUMMARY.......................................................................... 1 1 INTRODUCTION............................................................................. 3 2 PROJECT INFORMATION.............................................................. 4 2.1 Project Organization and Management Structure.................................. 4 2.2 Construction Progress................................................................................. 4 2.3 Mitigation Measures..................................................................................... 4 2.4 Status of License and Permit..................................................................... 4 3 SUMMARY OF EM&A REQUIREMENT........................................... 5 3.1 Air Quality....................................................................................................... 5 3.2 Noise............................................................................................................... 9 3.3 Water Quality............................................................................................... 12 4 MONITORING RESULT................................................................. 19 4.1 Air Quality.................................................................................................... 19 4.2 Noise............................................................................................................ 21 4.3 Water Quality Monitoring.......................................................................... 23 4.4 Summary of Project-Related Exceedances.......................................... 31 5 WASTE MANAGEMENT............................................................... 32 6 NON-COMPLIANCE AND
DEFICIENCY......................................... 33 6.1 Site Audit by ET.......................................................................................... 33 7 COMPLAINT................................................................................ 34 8 SUMMARY OF NOTIFICATION OF
SUMMONS, SUCCESSFUL PROSECUTIONS AND CORRECTIVE ACTIONS............................ 35 9 FUTURE KEY ISSUE................................................................... 36 |
|
|
|
|
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 June 2010
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
|
APPENDICES |
|
|
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 at
I-1, I-2, I-3 and Outfall; drilling and rock breaking for shaft excavation at
I-3; temporary rock drilling and installation at I-3; pre-bored H-pile drilling
for spiral ramp excavation at Outfall; structural steelwork erection for muck hopper and conveyor support at Outfall; excavation of man access shaft & vortex shaft at I-2; cascade and channel modification
concrete structure works at I-l; installation of noise enclosure to gantry crane structure at I-2 and Outfall; pipe jacking installation at Portion G at I-2; assembly of TBM, TBM drilling of the tunnel at Outfall; and erection of site office at Outfall within the reporting
month.
4.
No exceedances have been recorded for air quality and noise monitoring during the reporting month.
5.
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-2 on 9 June 2010. |
One recorded at I-1 on 21 June 2010. |
6.
The status
of waste generation in the reporting
month are:
·
A total of
2971.5 m
·
About 7.9 m3
general waste was disposed of to NENT Landfill;
·
About 400 kg paper/cardboard was recycled in the reporting month;
·
No metals was generated in the reporting month;
·
No plastic waste was disposed of in the reporting month; and
·
No chemical waste
was disposed of in the reporting month.
7.
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.
8.
As advised
by the Contractor and verified by ET:
·
No
non-compliance regarding the site inspection was received in the reporting
month;
·
No environmental complaint was
received during the reporting month; and
·
No summons
and prosecution was received in this reporting month.
9.
The major
construction works for the upcoming three months will be:
·
Site cleaning and tidying at I-1, I-2, I-3 and Outfall;
·
Erection of muck hopper and conveyor support steel structure at Outfall;
·
Drilling and excavation of man access shaft & vortex shaft at I-2;
·
Construction of approach channel structure at I-2;’
·
Cascade and channel modification concrete structure works at I-1;
·
Construction of skin wall at I-3;
·
Assembly of TBM, TBM drilling of the tunnel at Outfall;
·
Installation of noise enclosure at Outfall and I-2;
·
Pipe jacking installation at Portion G at I-2;
·
Mini-pile and pre-bored H-pile construction
at Portion G at I-2;
·
Drilling and excavation of spiral ramp at Outfall;
·
Drilling and excavation of vortex shaft at I-3;
1.1.1
The Drainage
Services Department (DSD) proposed to construct a tunnel with an internal
diameter of
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 twenty-seventh monthly EM&A report summarising the impact monitoring
results and audit findings of the EM&A program in June 2010.
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;
·
Drilling and rock breaking for shaft excavation at I-3;
·
Temporary rock dowel drilling and installation at I-3;
·
Pre-bored H-pile drilling for spiral ramp excavation at Outfall;
·
Structural steelwork erection for muck hopper and conveyor support at Outfall,
·
Excavation of man access shaft & vortex shaft at I-2;
·
Cascade and channel modification concrete structure works at I-1;
·
Installation of noise enclosure to gantry crane structure at I-2 and Outfall;
·
Pipe jacking installation at Portion G at I-2;
·
Assembly of TBM, TBM drilling of the tunnel at Outfall;
·
Erection of site office at Outfall.
2.2.1
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 - TE
|
Equipment Type |
Model |
Serial Number |
Calibration Orifice Number |
Location |
|
HVAS |
BM2000HX |
4994 |
1785 |
ASR 1 |
|
HVAS |
BM2000HX |
5875 |
1785 |
ASR 3 |
|
HVAS |
TE5005X |
1559 |
1785 |
ASR 8 |
|
HVAS |
TE5005X |
0646 |
1785 |
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
Monitoring Equipment and Calibration
3.2.5
Rion Precision Sound Level Meters of
Type NA-27 and Type NL
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 |
|
DO Meter |
YSI |
YSI 58 |
1 |
|
Turbidimeter |
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 stilling basin 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) & (ET) |
Outfall 1During Flood Tide and 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 |
*The upper stream location (I-3-C*) had
been relocated from end of February 2009 due to coarse stone blockage.
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 · 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
|
Station |
Monitoring Date |
Monitoring Result (mg/m3) |
Action/Limit Levels (mg/m3) |
|
ASR 1 |
01-Jun-10 |
62.0 |
307/500 |
|
55.6 |
|||
|
68.3 |
|||
|
07-Jun
-10 |
83.5 |
||
|
53.1 |
|||
|
99.9 |
|||
|
11-Jun-10 |
87.2 |
||
|
78.4 |
|||
|
79.7 |
|||
|
17-Jun-10 |
86.0 |
||
|
89.8 |
|||
|
48.0 |
|||
|
23-Jun-10 |
84.7 |
||
|
73.3 |
|||
|
94.8 |
|||
|
29-Jun-10 |
60.7 |
||
|
99.9 |
|||
|
62.0 |
|||
|
ASR 3 |
01-Jun
-10 |
122.3 |
327/500 |
|
71.9 |
|||
|
99.6 |
|||
|
07-Jun-10 |
74.4 |
||
|
55.5 |
|||
|
105.9 |
|||
|
11-Jun-10 |
138.7 |
||
|
126.1 |
|||
|
65.6 |
|||
|
17-Jun
-10 |
78.2 |
||
|
69.3 |
|||
|
65.6 |
|||
|
23-Jun-10 |
89.5 |
||
|
71.9 |
|||
|
81.9 |
|||
|
29-Jun-10 |
92.0 |
||
|
132.4 |
|||
|
83.2 |
|||
|
ASR 8 |
01-Jun-10 |
75.6 |
337/500 |
|
246.9 |
|||
|
198.3 |
|||
|
07-June-10 |
153.8 |
||
|
105.2 |
|||
|
103.9 |
|||
|
11-Jun-10 |
128.2 |
||
|
209.1 |
|||
|
107.9 |
|||
|
17-Jun-10 |
176.7 |
||
|
89.0 |
|||
|
98.5 |
|||
|
23-Jun-10 |
105.2 |
||
|
75.6 |
|||
|
58.0 |
|||
|
29-Jun-10 |
121.4 |
||
|
97.1 |
|||
|
64.8 |
|||
|
ASR 9 |
01-Jun-10 |
94.3 |
329/500 |
|
152.3 |
|||
|
172.5 |
|||
|
07-Jun-10 |
103.8 |
||
|
95.7 |
|||
|
87.6 |
|||
|
11-Jun-10 |
95.7 |
||
|
122.6 |
|||
|
114.5 |
|||
|
17-Jun-10 |
165.8 |
||
|
71.4 |
|||
|
57.9 |
|||
|
23-Jun-10 |
133.4 |
||
|
68.7 |
|||
|
62.0 |
|||
|
29-Jun-10 |
146.9 |
||
|
93.0 |
|||
|
63.3 |
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** |
01-Jun-10 |
64.9 |
70 |
|
07-Jun-10 |
63.0 |
65 |
|
|
17-Jun-10 |
63.2 |
65 |
|
|
23-Jun-10 |
63.9 |
70 |
|
|
29-Jun-10 |
63.4 |
70 |
|
|
NSR 3 |
01-Jun-10 |
64.5 |
75 |
|
07-Jun-10 |
72.8 |
||
|
17-Jun-10 |
66.9 |
||
|
23-Jun-10 |
67.9 |
||
|
29-Jun-10 |
68.3 |
||
|
NSR 6 |
01-Jun-10 |
68.0 |
|
|
07-Jun-10 |
67.7 |
||
|
17-Jun-10 |
58.1 |
||
|
23-Jun-10 |
64.9 |
||
|
29-Jun-10 |
56.7 |
||
|
NSR 8 |
01-Jun-10 |
64.8 |
|
|
07-Jun-10 |
63.8 |
||
|
17-Jun-10 |
63.3 |
||
|
23-Jun-10 |
64.9 |
||
|
29-Jun-10 |
62.2 |
||
|
NSR 9 |
01-Jun-10 |
64.0 |
|
|
07-Jun-10 |
68.4 |
||
|
17-Jun-10 |
63.9 |
||
|
23-Jun-10 |
68.1 |
||
|
29-Jun-10 |
65.0 |
Table 4-2 Noise Monitoring Results
**Noise Limit
level at NSR1 was reduced from 70
dB(A) to
65 dB(A) during examination periods
between 2 and 18 June 2010.
4.2.2
No exceedances
of Action and Limit Levels were recorded in our regular noise monitoring during
the reporting month.
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 |
Nil |
One
recorded on 21 June 2010. |
|
Total |
Nil |
1 |
Table 4-3 Summary of Exceedances for I-1
|
Parameter |
Action
Level Exceedance |
Limit
Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
One
recorded at I-2 on 9 June 2010. |
Nil |
|
Total |
1 |
Nil |
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
Two non-project
related exceedances were recorded for the water quality monitoring within the
reporting month.
4.3.4
The exceedance of Control Action Levels of SS (120% higher than I-2-C) recorded
at I-2 on 9 June 2010 was below baseline Action/Limit Levels
and was within the range of baseline SS concentration. Construction activities including site cleaning & tidying, erection
of noise enclosure at vortex drop shaft and man access shaft, excavation,
erection of working platform for mini-pile and pipe jacking were undertaken
during the measurement and no direct disturbance was observed from the site. Thus, the exceedance of SS levels recorded on 9 June 2010
at I-2 was considered to be contributed by natural variation and no action was
therefore required.
4.3.5
The exceedance of Baseline Action Levels of SS recorded at I-1 on 21 June 2010 was slightly above baseline Limit Level and above the
Control Limit Level. The measured value was still within the range of baseline
SS concentration. Construction activities including general site cleaning and
housekeeping; erect formwork for spiral ramp; strip off formwork for spiral
ramp; rebar fixing for spiral ramp and erect scaffold working platform for
spiral ramp were undertaken during the measurement and no direct disturbance
was observed from the site. Thus, the exceedance of SS levels recorded on 21
June 2010 at I-1 was considered to be contributed by natural variation and no
action was therefore required.
4.3.6
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 |
02-Jun-10 |
22.00 |
7.97 |
3.42 / 3.34 |
7.23 |
9.64 |
9.75 / 12.47 |
4.25 |
8.85 / 10.17 |
|
|
04-Jun-10 |
24.10 |
7.91 |
|
7.05 |
5.10 |
|
2.00 |
|
|
|
07-Jun-10 |
27.50 |
7.53 |
|
7.27 |
3.54 |
|
3.15 |
|
|
|
09-Jun-10 |
23.00 |
7.68 |
|
7.02 |
8.42 |
|
2.00 |
|
|
|
11-Jun-10 |
24.65 |
7.34 |
|
7.27 |
3.74 |
|
2.90 |
|
|
|
15-Jun-10 |
26.20 |
6.60 |
|
7.59 |
5.39 |
|
2.60 |
|
|
|
17-Jun-10 |
25.60 |
7.12 |
|
7.57 |
7.55 |
|
3.70 |
|
|
|
19-Jun-10 |
26.00 |
6.61 |
|
7.46 |
6.48 |
|
4.10 |
|
|
|
21-Jun-10 |
28.30 |
6.71 |
|
7.57 |
7.03 |
|
10.35 |
|
|
|
23-Jun-10 |
23.90 |
6.37 |
|
7.14 |
6.44 |
|
3.85 |
|
|
|
25-Jun-10 |
27.00 |
6.37 |
|
7.78 |
2.96 |
|
2.00 |
|
|
|
28-Jun-10 |
25.70 |
6.22 |
|
7.65 |
5.50 |
|
2.10 |
|
|
|
30-Jun-10 |
28.70 |
6.00 |
|
7.43 |
6.42 |
|
2.05 |
|
|
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 |
02-Jun-10 |
22.35 |
8.05 |
- / - |
7.21 |
9.47 |
- / - |
5.20 |
- / - |
|
|
04-Jun-10 |
23.95 |
7.90 |
|
7.02 |
5.25 |
|
2.00 |
|
|
|
07-Jun-10 |
27.95 |
7.48 |
|
7.26 |
3.68 |
|
2.90 |
|
|
|
09-Jun-10 |
23.50 |
7.75 |
|
7.05 |
8.64 |
|
2.00 |
|
|
|
11-Jun-10 |
24.35 |
7.28 |
|
7.25 |
3.81 |
|
2.65 |
|
|
|
15-Jun-10 |
26.05 |
6.68 |
|
7.50 |
8.18 |
|
7.25 |
|
|
|
17-Jun-10 |
25.50 |
7.05 |
|
7.61 |
7.71 |
|
4.65 |
|
|
|
19-Jun-10 |
25.75 |
6.54 |
|
7.41 |
6.65 |
|
4.10 |
|
|
|
21-Jun-10 |
28.50 |
6.66 |
|
7.61 |
7.12 |
|
6.50 |
|
|
|
23-Jun-10 |
24.00 |
6.45 |
|
7.16 |
6.58 |
|
3.30 |
|
|
|
25-Jun-10 |
26.60 |
6.50 |
|
7.84 |
3.45 |
|
2.35 |
|
|
|
28-Jun-10 |
25.25 |
6.13 |
|
7.61 |
5.40 |
|
2.00 |
|
|
|
30-Jun-10 |
28.60 |
6.07 |
|
7.40 |
6.58 |
|
3.70 |
|
|
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 |
02-Jun-10 |
23.20 |
8.00 |
3.66 / 3.63 |
7.07 |
5.00 |
6.63 / 6.99 |
4.45 |
7.68 / 8.34 |
|
|
04-Jun-10 |
24.00 |
8.02 |
|
7.12 |
2.22 |
|
2.00 |
|
|
|
07-Jun-10 |
27.20 |
7.58 |
|
7.40 |
2.03 |
|
2.00 |
|
|
|
09-Jun-10 |
24.00 |
7.68 |
|
7.07 |
4.26 |
|
2.55 |
|
|
|
11-Jun-10 |
24.90 |
7.08 |
|
7.40 |
1.77 |
|
2.45 |
|
|
|
15-Jun-10 |
26.20 |
6.86 |
|
7.66 |
1.93 |
|
2.00 |
|
|
|
17-Jun-10 |
25.95 |
6.81 |
|
7.48 |
1.89 |
|
2.00 |
|
|
|
19-Jun-10 |
26.00 |
6.51 |
|
7.56 |
2.54 |
|
2.00 |
|
|
|
21-Jun-10 |
28.00 |
6.44 |
|
7.50 |
2.11 |
|
2.00 |
|
|
|
23-Jun-10 |
23.00 |
5.48 |
|
7.21 |
6.19 |
|
3.30 |
|
|
|
25-Jun-10 |
27.50 |
6.13 |
|
7.52 |
3.08 |
|
2.80 |
|
|
|
28-Jun-10 |
26.30 |
6.13 |
|
7.54 |
4.54 |
|
5.20 |
|
|
|
30-Jun-10 |
28.10 |
6.15 |
|
7.25 |
2.58 |
|
2.50 |
|
|
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 |
02-Jun-10 |
22.95 |
8.06 |
- / - |
7.11 |
5.13 |
- / - |
5.35 |
- / - |
|
|
04-Jun-10 |
24.30 |
8.02 |
|
7.10 |
2.28 |
|
2.45 |
|
|
|
07-Jun-10 |
27.00 |
7.55 |
|
7.41 |
2.10 |
|
2.00 |
|
|
|
09-Jun-10 |
23.90 |
7.63 |
|
7.11 |
4.30 |
|
2.00 |
|
|
|
11-Jun-10 |
25.00 |
7.08 |
|
7.33 |
1.81 |
|
3.70 |
|
|
|
15-Jun-10 |
26.25 |
6.89 |
|
7.62 |
1.97 |
|
2.00 |
|
|
|
17-Jun-10 |
26.10 |
6.88 |
|
7.50 |
1.91 |
|
2.00 |
|
|
|
19-Jun-10 |
25.90 |
6.58 |
|
7.50 |
2.62 |
|
2.00 |
|
|
|
21-Jun-10 |
28.20 |
6.52 |
|
7.52 |
2.17 |
|
2.05 |
|
|
|
23-Jun-10 |
23.20 |
5.58 |
|
7.30 |
6.30 |
|
3.50 |
|
|
|
25-Jun-10 |
27.30 |
6.29 |
|
7.51 |
3.17 |
|
2.95 |
|
|
|
28-Jun-10 |
26.00 |
6.11 |
|
7.56 |
4.83 |
|
5.05 |
|
|
|
30-Jun-10 |
28.00 |
6.20 |
|
7.23 |
2.64 |
|
2.60 |
|
|
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 |
02-Jun-10 |
22.35 |
8.13 |
3.65 / 3.51 |
7.04 |
3.46 |
3.99 / 4.18 |
2.50 |
6.13 / 7.23 |
|
|
04-Jun-10 |
24.00 |
8.06 |
|
7.17 |
3.49 |
|
2.00 |
|
|
|
07-Jun-10 |
27.35 |
7.35 |
|
7.22 |
2.08 |
|
2.35 |
|
|
|
09-Jun-10 |
24.00 |
7.78 |
|
7.15 |
2.36 |
|
2.00 |
|
|
|
11-Jun-10 |
25.50 |
6.73 |
|
7.47 |
3.12 |
|
2.00 |
|
|
|
15-Jun-10 |
26.60 |
6.91 |
|
7.64 |
2.01 |
|
2.00 |
|
|
|
17-Jun-10 |
25.30 |
7.00 |
|
7.63 |
2.12 |
|
2.00 |
|
|
|
19-Jun-10 |
26.40 |
6.35 |
|
7.60 |
1.87 |
|
2.00 |
|
|
|
21-Jun-10 |
28.00 |
6.48 |
|
7.51 |
1.84 |
|
2.00 |
|
|
|
23-Jun-10 |
22.80 |
5.49 |
|
7.20 |
3.22 |
|
5.55 |
|
|
|
25-Jun-10 |
27.15 |
6.14 |
|
7.58 |
2.74 |
|
2.05 |
|
|
|
28-Jun-10 |
26.60 |
6.44 |
|
7.61 |
3.61 |
|
2.00 |
|
|
|
30-Jun-10 |
28.60 |
6.42 |
|
7.18 |
2.40 |
|
2.95 |
|
|
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 |
02-Jun-10 |
22.50 |
8.19 |
- / - |
7.06 |
3.56 |
- / - |
2.15 |
- / - |
|
|
04-Jun-10 |
24.10 |
8.12 |
|
7.15 |
3.51 |
|
2.00 |
|
|
|
07-Jun-10 |
27.00 |
7.22 |
|
7.20 |
2.08 |
|
2.00 |
|
|
|
09-Jun-10 |
23.75 |
7.74 |
|
7.08 |
2.49 |
|
2.00 |
|
|
|
11-Jun-10 |
25.20 |
6.84 |
|
7.45 |
3.15 |
|
2.00 |
|
|
|
15-Jun-10 |
26.00 |
7.01 |
|
7.61 |
2.12 |
|
2.00 |
|
|
|
17-Jun-10 |
25.50 |
7.03 |
|
7.62 |
2.16 |
|
2.00 |
|
|
|
19-Jun-10 |
26.20 |
6.42 |
|
7.61 |
1.94 |
|
2.00 |
|
|
|
21-Jun-10 |
27.80 |
6.57 |
|
7.48 |
1.88 |
|
2.00 |
|
|
|
23-Jun-10 |
22.70 |
5.50 |
|
7.10 |
3.37 |
|
6.15 |
|
|
|
25-Jun-10 |
27.40 |
6.14 |
|
7.55 |
2.81 |
|
2.00 |
|
|
|
28-Jun-10 |
26.50 |
6.36 |
|
7.57 |
3.66 |
|
2.00 |
|
|
|
30-Jun-10 |
28.80 |
6.64 |
|
7.16 |
2.58 |
|
2.60 |
|
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 June 2010. 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 |
25 |
0 |
0 |
0 |
0 |
|
Water |
78 |
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) |
2971.5 |
|
Inert C&D Material Reused in other Contracts* (m3) |
275.0 |
|
Metals Generated (kg) |
Nil |
|
Paper / Cardboard Packaging (kg) |
400 |
|
Plastics (kg) |
Nil |
|
Chemical Waste (kg) |
Nil |
|
General Waste Disposed of to NENT Landfill (m3) |
7.9 |
* Other Contracts
include DC/2007/17 and HY/2007/09.
Table 5-1 Waste Generated in June 2010
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 |
|
4 June
2010 |
1. The water treatment
system at Outfall was observed not function properly and the quality of the water discharge was required to improve. 2. The chemicals were
observed without drip tray at Outfall. |
1. The Contractor was reminded to regular maintain the water treatment system and to ensure the system functional
properly at Outfall. 2. The Contractor was reminded to provide drip tray for the
chemicals at Outfall. |
1.The water treatment
system was checked and the water quality at the Outfall discharge point was
improved as observed on 25 June 2010. (Closed) 2.The chemicals were found removed on 25 June 2010. (Closed) |
|
25
June 2010 |
1.
The tarpaulin on exposed slope at I3 was
observed broken. |
2.
The Contractor was reminded to provide the
tarpaulin properly cover
to minimize surface runoff. |
1.
The slope at I-3
was found covered with tarpaulin properly on 5 July 2010. (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
No
environmental complaint was received during the reporting month. Details of the complaint investigation can be referred to Appendix K.
7.1.3
Cumulative statistics of
environmental complaints are shown in Table 7-1.
|
Complaints Received in the Reporting Month |
Cumulative Number of Complaints |
|
0 |
17 |
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 |
||
|
June 2010 |
Cumulative |
June
2010 |
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;
·
Erection of muck hopper and conveyor support steel structure at Outfall;
·
Drilling and excavation of man access shaft & vortex shaft at I-2;
·
Construction of approach channel structure at I-2;’
·
Cascade and channel modification concrete structure works at I-1;
·
Construction of skin wall at I-3;
·
Assembly of TBM, TBM drilling of the tunnel at Outfall;
·
Installation of noise enclosure at Outfall and I-2;
·
Pipe jacking installation at Portion G at I-2;
·
Mini-pile and pre-bored H-pile construction
at Portion G at I-2;
·
Drilling and excavation of spiral ramp at Outfall;
·
Drilling and excavation of vortex shaft at I-3;
|
|
|
|
|
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 |