


|
|
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 October 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 and
breaking up exiting boulder at I-1, I-2, I-3 and Outfall, tree transplanting at
I-1, I-2 and I-3; socket H-piling and construction
of launching chamber at Outfall; soil nailing at I-1,
I-3 and Outfall; formation of access road
at I-3 and Outfall; Excavation and Lateral Support (ELS) at I-1; construction
of skin wall and formation 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, one exceedance of Limit level was recorded from EPD, and one environmental complaint on noise trigger the
excceedance of Action Level.
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 |
Nil |
Nil |
6.
No exceedance has been recorded for water quality monitoring during the
reporting month.
7.
The status
of waste generation in the reporting month are:
·
A total of 1,125.2
m3 C&D material was disposed of to public fill at Tuen Mun and 7, 480.0 m3
inert C&D materials were reused in other Contracts. Detail information
could be referred to Section 5.1.1 of this report.
·
About 2.9 m3
general waste was disposed of to NENT Landfill;
·
1,400 kg 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;
·
Two 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;
·
Socket H-piling at 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;
·
Formation
of steel platform at I-2
·
Formation
of shaft at I-2; and
·
Construction of 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 nineteenth monthly EM&A report summarising the impact monitoring results and
audit findings of the EM&A program in October 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 and I-3;
·
Socket H-piling at 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;
·
Excavation
and Lateral Support (ELS) at I-1;
·
Construction
of skin wall at I-2;
·
Formation
of steel platform at I-2; and
·
Construction of Launching Chamber at Outfall.
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 YSI |
PH/Oxi 340i YSI 58 |
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 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) |
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 |
*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 · 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 |
02-Oct-09 |
60.1 |
307/500 |
|
65.1 |
|||
|
52.8 |
|||
|
08-Oct-09 |
77.3 |
||
|
170.0 |
|||
|
127.5 |
|||
|
14-Oct-09 |
226.6 |
||
|
96.6 |
|||
|
122.3 |
|||
|
20-Oct-09 |
145.5 |
||
|
139.1 |
|||
|
91.4 |
|||
|
23-Oct-09 |
110.7 |
||
|
234.4 |
|||
|
105.6 |
|||
|
29-Oct-09 |
224.1 |
||
|
146.8 |
|||
|
179.0 |
|||
|
ASR 3 |
02-Oct-09 |
106.9 |
327/500 |
|
61.7 |
|||
|
56.2 |
|||
|
08-Oct-09 |
86.9 |
||
|
178.7 |
|||
|
119.9 |
|||
|
14-Oct-09 |
221.5 |
||
|
104.0 |
|||
|
129.7 |
|||
|
20-Oct-09 |
139.5 |
||
|
105.2 |
|||
|
72.2 |
|||
|
23-Oct-09 |
153.0 |
||
|
142.0 |
|||
|
153.0 |
|||
|
29-Oct-09 |
127.3 |
||
|
85.7 |
|||
|
126.0 |
|||
|
ASR 8 |
02-Oct-09 |
62.0 |
337/500 |
|
72.8 |
|||
|
76.9 |
|||
|
08-Oct-09 |
129.1 |
||
|
145.9 |
|||
|
120.0 |
|||
|
14-Oct-09 |
180.7 |
||
|
149.7 |
|||
|
91.6 |
|||
|
20-Oct-09 |
92.9 |
||
|
179.4 |
|||
|
85.2 |
|||
|
23-Oct-09 |
126.5 |
||
|
174.2 |
|||
|
147.1 |
|||
|
29-Oct-09 |
265.9 |
||
|
140.7 |
|||
|
169.1 |
|||
|
ASR 9 |
02-Oct-09 |
65.9 |
329/500 |
|
59.0 |
|||
|
57.8 |
|||
|
08-Oct-09 |
129.3 |
||
|
128.0 |
|||
|
119.8 |
|||
|
14-Oct-09 |
196.1 |
||
|
111.6 |
|||
|
141.6 |
|||
|
20-Oct-09 |
130.7 |
||
|
132.1 |
|||
|
132.1 |
|||
|
23-Oct-09 |
104.8 |
||
|
136.2 |
|||
|
93.9 |
|||
|
29-Oct-09 |
230.1 |
||
|
129.3 |
|||
|
145.7 |
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 |
08-Oct-09 |
67.7 |
70/65** |
|
14-Oct-09 |
64.9 |
||
|
20-Oct-09 |
69.3 |
||
|
29-Oct-09 |
64.0 |
||
|
NSR 3 |
08-Oct-09 |
72.5 |
75 |
|
14-Oct-09 |
68.4 |
||
|
20-Oct-09 |
62.1 |
||
|
29-Oct-09 |
62.6 |
||
|
NSR 6 |
08-Oct-09 |
53.0 |
|
|
14-Oct-09 |
58.4 |
||
|
20-Oct-09 |
61.7 |
||
|
29-Oct-09 |
63.2 |
||
|
NSR 8 |
02-Oct-09* |
66.2 |
|
|
06-Oct-09* |
68.0 |
||
|
08-Oct-09 |
66.8 |
||
|
14-Oct-09 |
66.0 |
||
|
16-Oct-09* |
66.6 |
||
|
20-Oct-09 |
67.9 |
||
|
29-Oct-09 |
65.7 |
||
|
NSR 9 |
02-Oct-09* |
73.7 |
|
|
06-Oct-09* |
71.2 |
||
|
08-Oct-09 |
71.3 |
||
|
14-Oct-09 |
70.7 |
||
|
16-Oct-09* |
71.8 |
||
|
20-Oct-09 |
72.5 |
||
|
23-Oct-09* |
72.0 |
||
|
29-Oct-09 |
63.2 |
||
|
31-Oct-09* |
67.6 |
*
Additional noise monitoring due to the documented complaints.
** Noise Limit Level
at NSR 1 was reduced from 70 dB(A) to 65 dB(A) during the examination period
from 29 – 30 October 2009.
Table 4-2 Noise Monitoring Results
4.2.2
One
complaint was received on 2 October
2009 regarding the daytime construction noise at the Outfall construction site.
Hence, it would be an Action Level exceedance. Details of the complaint are
presented in Section 7. Besides, two consecutive noise measurements were carried out by EPD at NSR
9 on 28 October 2009. The measured noise levels were 76.6 dB(A) and 75.9 dB(A).
Hence, they would be the Limit Level exceedances. Two possible reasons were
identified for the exceedance: 1. One of
the existing bamboo noise barrier was removed due to removal of the berm under
this existing noise barrier. 2. Comparing with the previous noise monitoring
results, number of PMEs (i.e. breaker) was increased and the PMEs were also
fully utilized simultaneously. For
mitigation measures, noise enclosure was used to cover the ceiling of the
portal, scaffolding of noise acoustic material was relocated, noise barriers
will be placed as closer as the breaker and the drilling rig during operation
and in addition, the number of breakers would be reduced. By the end of the reporting period, noise
mitigation proposal was submitted by the Contractor and under reviewed by ET
and IEC. Details of the Limit Level exceedances
are presented in the notification of exceedances were
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 |
Nil |
Nil |
|
Total |
Nil |
Nil |
Table 4-3 Summary of Exceedances for I-1
|
Parameter |
Action
Level Exceedance |
Limit
Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
Nil |
Nil |
|
Total |
Nil |
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
No
exceedance was recorded for the water quality monitoring within the reporting
period.
|
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-Oct-09 |
27.50 |
7.38 |
3.42 / 3.34 |
7.67 |
2.38 |
9.75 / 12.47 |
2.0 |
8.85 / 10.17 |
|
|
05-Oct-09 |
28.00 |
7.64 |
|
7.51 |
1.94 |
|
2.7 |
|
|
|
07-Oct-09 |
28.20 |
7.84 |
|
7.63 |
1.97 |
|
2.0 |
|
|
|
09-Oct-09 |
28.30 |
7.65 |
|
7.59 |
2.52 |
|
2.0 |
|
|
|
12-Oct-09 |
26.25 |
7.57 |
|
7.50 |
4.53 |
|
3.2 |
|
|
|
14-Oct-09 |
27.60 |
7.84 |
|
7.58 |
2.82 |
|
2.0 |
|
|
|
16-Oct-09 |
27.70 |
7.65 |
|
7.43 |
2.51 |
|
5.1 |
|
|
|
19-Oct-09 |
27.00 |
7.74 |
|
7.40 |
7.08 |
|
8.3 |
|
|
|
21-Oct-09 |
27.10 |
7.72 |
|
7.60 |
1.91 |
|
2.0 |
|
|
|
23-Oct-09 |
26.55 |
7.49 |
|
7.33 |
1.39 |
|
2.0 |
|
|
|
27-Oct-09 |
26.85 |
7.72 |
|
7.23 |
2.99 |
|
4.0 |
|
|
|
29-Oct-09 |
24.75 |
7.74 |
|
7.22 |
3.08 |
|
4.4 |
|
|
|
31-Oct-09 |
24.20 |
7.79 |
|
7.33 |
2.24 |
|
5.1 |
|
|
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 |
02-Oct-09 |
27.70 |
7.50 |
- / - |
7.68 |
2.62 |
- / - |
2.0 |
- / - |
|
|
05-Oct-09 |
27.80 |
7.70 |
|
7.50 |
2.11 |
|
2.3 |
|
|
|
07-Oct-09 |
28.30 |
7.91 |
|
7.65 |
2.06 |
|
2.0 |
|
|
|
09-Oct-09 |
28.50 |
7.55 |
|
7.60 |
2.65 |
|
2.0 |
|
|
|
12-Oct-09 |
26.55 |
7.59 |
|
7.52 |
4.73 |
|
3.1 |
|
|
|
14-Oct-09 |
27.95 |
7.77 |
|
7.55 |
2.92 |
|
2.0 |
|
|
|
16-Oct-09 |
27.55 |
7.76 |
|
7.42 |
2.74 |
|
4.8 |
|
|
|
19-Oct-09 |
27.10 |
7.82 |
|
7.42 |
7.26 |
|
8.4 |
|
|
|
21-Oct-09 |
26.95 |
7.79 |
|
7.44 |
2.05 |
|
2.0 |
|
|
|
23-Oct-09 |
27.00 |
7.51 |
|
7.35 |
1.44 |
|
2.0 |
|
|
|
27-Oct-09 |
27.80 |
7.80 |
|
7.24 |
3.22 |
|
4.7 |
|
|
|
29-Oct-09 |
24.95 |
7.82 |
|
7.22 |
3.22 |
|
4.2 |
|
|
|
31-Oct-09 |
24.00 |
7.88 |
|
7.33 |
2.52 |
|
4.3 |
|
|
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 |
02-Oct-09 |
27.50 |
7.43 |
3.66 / 3.63 |
7.60 |
2.28 |
6.63 / 6.99 |
2.4 |
7.68 / 8.34 |
|
|
05-Oct-09 |
28.10 |
7.58 |
|
7.52 |
1.20 |
|
2.0 |
|
|
|
07-Oct-09 |
28.60 |
7.66 |
|
7.61 |
1.26 |
|
2.0 |
|
|
|
09-Oct-09 |
28.60 |
7.48 |
|
7.71 |
1.04 |
|
2.0 |
|
|
|
12-Oct-09 |
26.00 |
7.68 |
|
7.66 |
1.54 |
|
2.0 |
|
|
|
14-Oct-09 |
27.45 |
7.36 |
|
7.52 |
1.26 |
|
2.0 |
|
|
|
16-Oct-09 |
27.55 |
7.73 |
|
7.42 |
2.32 |
|
2.0 |
|
|
|
19-Oct-09 |
27.00 |
7.77 |
|
7.36 |
2.61 |
|
2.4 |
|
|
|
21-Oct-09 |
27.45 |
7.43 |
|
7.42 |
1.20 |
|
2.0 |
|
|
|
23-Oct-09 |
26.75 |
7.51 |
|
7.28 |
1.39 |
|
2.0 |
|
|
|
27-Oct-09 |
26.15 |
7.82 |
|
7.33 |
1.47 |
|
2.0 |
|
|
|
29-Oct-09 |
24.35 |
7.63 |
|
7.26 |
1.60 |
|
2.0 |
|
|
|
31-Oct-09 |
23.85 |
7.84 |
|
7.35 |
1.37 |
|
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 |
02-Oct-09 |
27.10 |
7.58 |
- / - |
7.57 |
2.41 |
- / - |
3.1 |
- / - |
|
|
05-Oct-09 |
28.20 |
7.65 |
|
7.52 |
1.39 |
|
2.0 |
|
|
|
07-Oct-09 |
28.20 |
7.76 |
|
7.60 |
1.37 |
|
2.0 |
|
|
|
09-Oct-09 |
28.40 |
7.61 |
|
7.67 |
1.13 |
|
2.0 |
|
|
|
12-Oct-09 |
26.00 |
7.67 |
|
7.61 |
1.63 |
|
2.0 |
|
|
|
14-Oct-09 |
27.35 |
7.47 |
|
7.53 |
1.35 |
|
2.0 |
|
|
|
16-Oct-09 |
27.75 |
7.81 |
|
7.42 |
2.44 |
|
2.0 |
|
|
|
19-Oct-09 |
27.20 |
7.84 |
|
7.36 |
2.68 |
|
2.0 |
|
|
|
21-Oct-09 |
27.20 |
7.53 |
|
7.42 |
1.31 |
|
2.0 |
|
|
|
23-Oct-09 |
26.95 |
7.52 |
|
7.23 |
1.46 |
|
2.0 |
|
|
|
27-Oct-09 |
26.20 |
7.69 |
|
7.34 |
1.56 |
|
2.0 |
|
|
|
29-Oct-09 |
24.50 |
7.70 |
|
7.26 |
1.63 |
|
2.0 |
|
|
|
31-Oct-09 |
23.75 |
7.85 |
|
7.34 |
1.49 |
|
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 |
02-Oct-09 |
27.80 |
7.68 |
3.65 / 3.51 |
7.55 |
2.72 |
3.99 / 4.18 |
2.4 |
6.13 / 7.23 |
|
|
05-Oct-09 |
28.10 |
7.39 |
|
7.47 |
1.79 |
|
2.0 |
|
|
|
07-Oct-09 |
28.35 |
7.98 |
|
7.56 |
1.53 |
|
2.0 |
|
|
|
09-Oct-09 |
28.55 |
7.40 |
|
7.66 |
1.23 |
|
2.0 |
|
|
|
12-Oct-09 |
26.10 |
7.77 |
|
7.60 |
1.49 |
|
2.0 |
|
|
|
14-Oct-09 |
27.30 |
7.53 |
|
7.43 |
1.85 |
|
2.0 |
|
|
|
16-Oct-09 |
27.60 |
7.75 |
|
7.43 |
1.59 |
|
2.0 |
|
|
|
19-Oct-09 |
27.40 |
7.63 |
|
7.56 |
1.25 |
|
2.0 |
|
|
|
21-Oct-09 |
27.00 |
7.57 |
|
7.45 |
1.24 |
|
2.0 |
|
|
|
23-Oct-09 |
26.75 |
7.50 |
|
7.33 |
1.62 |
|
2.0 |
|
|
|
27-Oct-09 |
26.35 |
7.09 |
|
7.33 |
1.23 |
|
2.0 |
|
|
|
29-Oct-09 |
24.65 |
8.00 |
|
7.23 |
1.60 |
|
2.0 |
|
|
|
31-Oct-09 |
24.85 |
7.78 |
|
7.33 |
1.28 |
|
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 |
02-Oct-09 |
27.75 |
7.66 |
- / - |
7.57 |
2.88 |
- / - |
2.0 |
- / - |
|
|
05-Oct-09 |
28.20 |
7.46 |
|
7.50 |
1.84 |
|
2.0 |
|
|
|
07-Oct-09 |
28.50 |
7.90 |
|
7.57 |
1.61 |
|
2.0 |
|
|
|
09-Oct-09 |
28.80 |
7.57 |
|
7.65 |
1.42 |
|
2.0 |
|
|
|
12-Oct-09 |
26.20 |
7.68 |
|
7.59 |
1.55 |
|
2.0 |
|
|
|
14-Oct-09 |
27.70 |
7.50 |
|
7.44 |
1.98 |
|
2.0 |
|
|
|
16-Oct-09 |
27.60 |
7.75 |
|
7.42 |
1.81 |
|
2.0 |
|
|
|
19-Oct-09 |
27.30 |
7.70 |
|
7.64 |
1.43 |
|
2.0 |
|
|
|
21-Oct-09 |
26.85 |
7.60 |
|
7.44 |
1.38 |
|
2.0 |
|
|
|
23-Oct-09 |
27.05 |
7.47 |
|
7.33 |
1.71 |
|
2.0 |
|
|
|
27-Oct-09 |
26.30 |
7.18 |
|
7.33 |
1.41 |
|
2.0 |
|
|
|
29-Oct-09 |
24.60 |
8.11 |
|
7.23 |
1.66 |
|
2.0 |
|
|
|
31-Oct-09 |
24.65 |
7.77 |
|
7.33 |
1.41 |
|
2.0 |
|
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 October 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 |
30* |
1
(Complaint) |
3.3 |
2 |
6.7 |
|
Water |
78 |
0 |
0 |
0 |
0 |
* Two noise measurements were carried
by EPD on 28 October 2009.
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) |
1,125.2 |
|
Inert C&D Material Reused in other Contracts* (m3) |
7,480.0 |
|
Metals Generated (kg) |
Nil |
|
Paper / Cardboard Packaging (kg) |
1,400.0 |
|
Plastics (kg) |
Nil |
|
Chemical Waste (kg) |
Nil |
|
General Waste Disposed of to NENT Landfill (m3) |
2.9 |
* Other Contracts include DC/2007/08,
DC/2007/17, DC/2007/06, DC/2006/04,
Table 5-1 Waste Generated in October 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 |
|
8
October 2009 |
1. Discharged water containing silt and sediment was
observed at Outfall. 2. Movable noise barrier was observed not maintained
in good condition. 3. The wrapping materials at the breaking tip was
observed not maintained in good condition. |
1. The Contractor was reminded to remove silt and sediment before discharge water. 2. The
Contractor was reminded to maintain the
movable noise barrier in good condition. 3. The
Contractor was reminded to maintain the
wrapping materials at the breaking tip in good condition |
1. During
site inspection on 30 October 2009, the discharge water was was free of silt and sediment.
(Closed) 2. During
site inspection on 30 October 2009, the movable noise barrier was maintained in good
condition at Outfall. (Closed) 3. During
site inspection on 30 October 2009, the wrapping materials at the breaking tip was
maintained in good condition at Outfall. (Closed) |
|
30 October
2009 |
1. The
site was observed to be dusty at I-3. |
1. The
Contractor was reminded to provide water
spraying to dusty areas regularly. |
1. During
the site inspection on 5 November 2009,
water spraying was provided at I-3. |
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
Two
complaints were received during the reporting month.
7.1.3
One environmental complaint was received
by SOR on 2 October regarding daytime
construction noise exceedance recorded at Greenview Terrace (NSR9) on 24
September 2009 at the
outfall construction site. According to the regular noise monitoring from July to October 2009, all measured noise levels were below the Limit Levels. Additional noise measurements taken on 2, 6,
16, 23 and 31 October 2009 (refers to * Additional
noise monitoring due to the documented complaints.
** Noise Limit Level
at NSR 1 was reduced from 70 dB(A) to 65 dB(A) during the examination period
from 29 – 30 October 2009.
7.1.4
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 were carried
out for reminding that the movable barrier should be placed to the breaking
activities as much as possible, movable noise barriers had been placed on site
and the movable noise barriers were modified, a joint filler wall was 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 maintained twice per week until no further complaint from Greenview
Terrace. Detail of the complaint investigation can be referred to Appendix K.
7.1.5
One environmental complaint was received by EPD on 6 October 2009
regarding the construction dust at I-3 on 2 October 2009. There is no
representative air monitoring location as stated in the EM&A Manual. The
contractor and the environmental team carried out site investigation on the
subject area at 8 October 2009 in response to the complaint. Air quality
mitigation measures as recommended in EIA have been implemented by the
Contractor, such as water spraying was provided to the exposed surface and
during excavation and loading/unloading works. The complaint for dust was
considered justifiable because it was due to windy
erosion on the
exposed surface. In view of the recent dry season, the haul road and the exposed
area would be dry very quickly. The Contractor was recommended to provide water
spraying more frequently especially in the dry season. Detail of the complaint
investigation can be referred to Appendix K.
7.1.6
Cumulative statistics of
environmental complaints are shown in Table 7-1.
|
Complaints Received in the Reporting Month |
Cumulative Number of Complaints |
|
2 |
12 |
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 |
||
|
October 09 |
Cumulative |
October 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;
·
Socket H-piling at 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;
·
Formation
of steel platform at I-2
·
Formation
of shaft at I-2; and
· Construction of 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 |
|
|
|
Appendix K |
|
|
|
Complaint Log |