



|
|
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 Summary
of Exceedances for O-1(FT)
Table 4-7 Summary
of Exceedances for O-1(ET)
Table 4-8 Water
Quality Monitoring Results
Table 4-9 Summary of Project-Related Exceedances
Table 5-1 Waste
Generated in December 2010
Table 6-1 Site Inspection by ET
Table 7-1 Cumulative Statistic of Environmental Complaint
|
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 five 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 Tsuen Wan Drainage Tunnel included
site cleaning and tidying at I-1, I-2, I-3 and Outfall, drilling, excavation
and rock splitting at spiral ramp at Outfall, pre-bored H-pile drilling and
soil nailing for CPR box culvert construction at Outfall, TBM (Tunnel boring
machine) drilling of the tunnel and mucking out of tunnel spoil at Outfall,
removal of sea wall and amour rock for basin scheme at Portion E, drilling and
excavation of vortex shaft at I-3, temporary rock dowel drilling and
installation at I-3, construction of pre-bored H-Pile for PB Wall at I-3,
construction of footing for erecting the tower crane at I-3, drilling,
excavation and rock splitting of man access shaft and vortex drop shaft at I-2,
preparation work for retaining wall at I-2, pipe jacking at Portion G at I-2,
construction of approach channel structure at I-2, erection of temporary steel
platform for H-pile wall at Portion G at I-2, cascade and channel modification
concrete structure works at I-1, horizontal drilling at I-1, and backfilling of
spiral ramp centre void at I-1 within the reporting month.
4.
No exceedances have been recorded for air quality monitoring during
the reporting month.
5.
No exceedances have been recorded for noise monitoring during the reporting month.
6.
Exceedances
for river water quality monitoring are summarised in the following table:
|
Parameter |
Action Level Exceedance |
Limit Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
One
record at I-1 on 1 Dec 2010 and one record at I-2 on 31 Dec 2010. |
Two
records at I-2 on 6 and 24 Dec 2010 and one record at I-3 on 24 Dec 2010. |
7.
Exceedances
for marine water quality monitoring are summarized in the following table:
|
Parameter |
Action Level Exceedance |
Limit Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
Two records at O-1(FT) on 3 and 22 Dec 2010 and one record at O-1(ET)
on 24 Dec 2010. |
Three
records at O-1(FT) on 1, 15 and 29 Dec 2010 and three records at O-1(ET) on
13, 15 and 29 Dec 2010. |
8.
The status
of waste generation in the reporting month are:
·
A total of
12,684.6 m
·
About 56.0
m3 general waste was disposed of to NENT Landfill;
·
About 400.0 kg paper/cardboard was recycled in the reporting month;
·
About 18 kg metal was
generated in the reporting month;
·
About 20 kg plastic waste was
disposed of in the reporting month; and
·
About 7450.2 kg chemical waste
was disposed of in the reporting month.
9.
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
site inspection checklists, were passed to the Contractor together with the ET’s
recommendations.
10.
As advised
by the Contractor and verified by ET:
·
No
non-compliance regarding the site inspection was received in the reporting
month;
·
No environmental noise
complaint was received during the reporting month; and
·
No summons
and prosecution was received in the reporting month.
11.
The major
construction works for the upcoming three months will be:
·
Site cleaning and tidying at I-1, I-2, I-3 and Outfall;
·
TBM drilling of the tunnel and mucking out of tunnel spoil
at Outfall;
·
Drilling, excavation and rock splitting at spiral ramp at
Outfall;
·
Pre-bored H-pile drilling, excavation and soil nailing for
CPR box culvert construction at Outfall;
·
Removal of sea wall and armour rocks for basin scheme at
Outfall Portion E;
·
Installation of marine sea wall block and amour rock for
basin scheme at Portion E;
·
Construction of PB wall at I-3;
·
Erection of tower crane at I-3;
·
Drilling and excavation of vortex shaft at I-3;
·
Pipe jacking at Portion G at I-2;
·
Construction of retaining wall at I-2;
·
Pre-bored H-pile construction for skin wall at Portion G at
I-2;
·
Construction for skin wall at Portion G at I-2;
·
Drilling, excavation and rock splitting of man access shaft
and vortex drop shaft at I-2;
·
Construction of approach channel structure at I-2;
·
Cascade and channel modification concrete structure works at
I-1;
·
Horizontal drilling at I-1; and
·
Backfilling of spiral ramp centre void at I-1.
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 programme 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
thirty-third monthly EM&A report summarising the impact monitoring results
and audit findings of the EM&A program in December 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:
l
Site cleaning and tidying at I-1, I-2, I-3 and Outfall;
l
Drilling, excavation and rock splitting at spiral ramp at
Outfall;
l
Pre-bored H-pile drilling and soil nailing for CPR box
culvert construction at Outfall;
l
TBM drilling of the tunnel and mucking out of tunnel spoil
at Outfall;
l
Removal of sea wall and amour rock for basin scheme at
Portion E;
l
Drilling and excavation of vortex shaft at I-3;
l
Temporary rock dowel drilling and installation at I-3;
l
Construction of pre-bored H-Pile for PB Wall at I-3;
l
Construction of footing for erecting the tower crane at I-3;
l
Drilling, excavation and rock splitting of man access shaft
and vortex drop shaft at I-2;
l
Preparation work for retaining wall at I-2;
l
Pipe jacking at Portion G at I-2;
l
Construction of approach channel structure at I-2;
l
Erection of temporary steel platform for H-pile wall at
Portion G at I-2;
l
Cascade and channel modification concrete structure works at
I-1;
l
Horizontal drilling at I-1; and
l
Backfilling of spiral ramp centre void at I-1.
2.2.3
Marine dredging for basin scheme at Portion E was conducted in
December 2010. The daily marine mud
dredging rate, as confirmed by the Contractor, was from 104 to 276 m3.
2.2.4
No open 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
One-hour total
suspended particulates (TSP) levels were 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
One-hour
TSP monitoring was 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 was 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 was kept in a clean and tightly
sealed plastic bag. The filter paper was then re-conditioned in desiccators for
24 hours before obtaining the weight under laboratory conditions.
3.1.4
The average
concentrations of the TSP were 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
were 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 was carried out by ALS Technichem (HK) Pty Limited (HOKLAS Registration Number
066).
Monitoring Equipment and Calibration
3.1.6
High Volume
Air Samplers (HVASs) were 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
were 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 was 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 |
1059 |
1785 |
ASR 8 |
|
HVAS |
TE5005X |
1713 |
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-hour 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 was
measured in terms of equivalent A-weighted sound pressure level (Leq)
measured in decibels (dB(A)). Monitoring
of Leq(30 min) was 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, were also recorded during monitoring. Major noise sources observed, both on-site
and off-site, were recorded on the field data sheet. All measurements were 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, were used. Noise levels for the A-weighted levels Leq(30min),
L10 and L90 were measured throughout the impact
monitoring. An average, by sound power,
of six consecutive 5 minutes readings was 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)
was applied to the measurements that were 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 were 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 NL-31 and B&K Integrating Sound Level Meter of Type 2238 in compliance
with the International Electrotechnical Commission Publication specifications
(Paragraph 3.2.3) were 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 was checked using an
acoustic calibrator (B&K 4231) generating a known sound pressure level at a
known frequency. Measurements were
considered as valid only if the calibration levels from before and after the
noise measurement agreed to within 1.0 dB(A).
Sound level meters and calibrators were calibrated annually to ensure
they performed to the same level of accuracy as stated in the manufacturer’s
specifications. The noise monitoring
equipments used during the reporting month are 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 |
NL-31 |
00410224 |
NSR1,
NSR3, NSR6, NSR8 and NSR9 |
|
Sound
Level Meter |
B&K |
2238 |
2562782 |
|
|
Sound
Level Meter |
B&K |
2238 |
2448529 |
|
|
Sound
Level Calibrator |
B&K |
4231 |
2699361 |
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* (since 16 July 2009) |
* The noise monitoring location of NSR9 had been adjusted
to rooftop since 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 hours) at these
NSRs. In order to ensure proper control of groundborne noise is executed by the
contractor, a monitoring requirement is recommended at the Hong Hoi Chee Hong
Temple at Intake 2 and Squatters at Intake 3 for compliance checking. According to the monitoring schedule, TBM
operation will be carried out for about 3 months in the vicinity of Hong Hoi
Chee Hong Temple at Intake 2 and Squatters at Intake 3. If groundborne noise criterion is exceeded,
the monitoring shall continue daily until acceptance has been restored against
the criterion. Otherwise the monitoring
can be discontinued.
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 hours 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 and 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 were measured at all designated monitoring
locations including control points at an interval of 3 days per week. DO,
temperature, turbidity, pH and SS measurements were undertaken at designated
monitoring locations.
3.3.5
It should be noted that water
samples for all monitoring parameters were collected, stored, preserved and
analysed according to Standard Methods, APHA 17 ed. and/or methods agreed by
the Director of Environmental Protection.
3.3.6
Each sample
was 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. 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 were transferred to clearly labelled and pre-cleaned sample containers
with necessary preservatives immediately after collection. The sample containers were provided by a
HOKLAS accredited laboratory. About 1 L
of samples was collected for all laboratory analysis. Following sampling, samples should be stored in a cool box at
temperature between 0 and 4 oC, 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 |
|
Turbidimeter |
EUTECH |
TN-100 |
1 |
Table 3‑9 Water Quality Monitoring Equipment
3.3.8
All pH
meters, DO meters and turbidimeters were checked and calibrated prior to
use. DO meters and turbidimeters were
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 were
checked with certified standard solutions before each use. Wet bulb calibrations for all DO meters were
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" was observed. The
calibration certificates are included in Appendix F.
3.3.9
Five designated impact monitoring locations (three river stations and two
marine stations) and five control locations (three river control stations and
two marine stations) were identified in the contract specific EM&A Manual for river and
marine water quality monitoring. These monitoring stations are listed in Table 3-10 below and shown in Appendix G.
|
Monitoring Station ID |
Name of Premises |
|
River
|
|
|
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 |
|
Marine |
|
|
O-1 (FT) and (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 were 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 was sampled during each sampling.
Control station to be sampled was 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 would 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 and Bottom) |
Surface
and Middle 5%-ile
of baseline data for surface and
middle layer. Bottom 5%-ile
of baseline data for bottom layer. |
Surface
and 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 limit.
·
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 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 0.1 mg/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 |
01-Dec-10 |
200.5 |
307/500 |
|
177.7 |
|||
|
195.4 |
|||
|
07-Dec-10 |
241.1 |
||
|
144.7 |
|||
|
218.3 |
|||
|
13-Dec-10 |
253.8 |
||
|
152.3 |
|||
|
176.4 |
|||
|
17-Dec-10 |
73.6 |
||
|
99.0 |
|||
|
86.3 |
|||
|
23-Dec-10 |
116.8 |
||
|
109.1 |
|||
|
92.6 |
|||
|
29-Dec-10 |
43.2 |
||
|
35.5 |
|||
|
35.5 |
|||
|
ASR 3 |
01-Dec-10 |
114.3 |
327/500 |
|
117.9 |
|||
|
134.7 |
|||
|
07-Dec-10 |
179.2 |
||
|
145.5 |
|||
|
230.9 |
|||
|
13-Dec-10 |
194.8 |
||
|
193.6 |
|||
|
205.7 |
|||
|
17-Dec-10 |
114.3 |
||
|
98.6 |
|||
|
77.0 |
|||
|
23-Dec-10 |
122.7 |
||
|
120.3 |
|||
|
89.0 |
|||
|
29-Dec-10 |
26.5 |
||
|
34.9 |
|||
|
49.3 |
|||
|
ASR 8 |
01-Dec-10 |
202.3 |
337/500 |
|
198.4 |
|||
|
227.4 |
|||
|
07-Dec-10 |
190.4 |
||
|
167.9 |
|||
|
235.4 |
|||
|
13-Dec-10 |
109.8 |
||
|
197.0 |
|||
|
197.0 |
|||
|
17-Dec-10 |
144.1 |
||
|
84.6 |
|||
|
138.8 |
|||
|
23-Dec-10 |
153.4 |
||
|
141.5 |
|||
|
125.6 |
|||
|
29-Dec-10 |
30.4 |
||
|
47.6 |
|||
|
194.4 |
|||
|
ASR 9 |
01-Dec-10 |
166.9 |
329/500 |
|
219.9 |
|||
|
238.9 |
|||
|
07-Dec-10 |
237.5 |
||
|
195.4 |
|||
|
263.3 |
|||
|
13-Dec-10 |
176.4 |
||
|
215.8 |
|||
|
194.1 |
|||
|
17-Dec-10 |
223.9 |
||
|
118.1 |
|||
|
115.4 |
|||
|
23-Dec-10 |
218.5 |
||
|
120.8 |
|||
|
58.4 |
|||
|
29-Dec-10 |
49.8 |
||
|
166.9 |
|||
|
48.9 |
Note: Italic indicates the occurrence of exceedance of Action level
Bold indicates
the occurrence of exceedance of Limit Level
Table 4-1 Air
Quality Monitoring Results
4.1.3
No project related air quality
exceedance was recorded in the reporting month.
4.2.1
The noise monitoring schedule of the
reporting period is given in Appendix H.
In response to the two complaints on construction noise received on 17
November 2010, additional noise measurements were conducted at NSR 9 on 9 and
15 December 2010. 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. Detailed 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-Dec-10 |
64.2 |
70 |
|
07-Dec-10 |
63.8 |
65 |
|
|
13-Dec-10 |
63.4 |
||
|
23-Dec-10 |
64.8 |
70 |
|
|
29-Dec-10 |
64.7 |
||
|
NSR 3 |
01-Dec-10 |
60.1 |
75 |
|
07-Dec-10 |
65.2 |
||
|
13-Dec-10 |
70.5 |
||
|
23-Dec-10 |
61.5 |
||
|
29-Dec-10 |
58.5 |
||
|
NSR 6 |
01-Dec-10 |
67.1 |
|
|
07-Dec-10 |
69.4 |
||
|
13-Dec-10 |
61.8 |
||
|
23-Dec-10 |
64.4 |
||
|
29-Dec-10 |
64.6 |
||
|
NSR 8 |
01-Dec-10 |
66.7 |
|
|
07-Dec-10 |
67.8 |
||
|
13-Dec-10 |
62.1 |
||
|
23-Dec-10 |
63.6 |
||
|
29-Dec-10 |
62.8 |
||
|
NSR 9 |
01-Dec-10 |
71.1 |
|
|
07-Dec-10 |
70.5 |
||
|
09-Dec-10* |
70.0 |
||
|
13-Dec-10 |
67.9 |
||
|
15-Dec-10* |
69.1 |
||
|
23-Dec-10 |
71.0 |
||
|
29-Dec-10 |
72.4 |
Note: * means additional noise monitoring
Table
4-2 Noise Monitoring Results
4.2.2
No
exceedances of Action and Limit Levels were recorded in our 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 4-7.
|
Parameter |
Action
Level Exceedance |
Limit
Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
One record on 1 Dec 2010 |
Nil |
|
Total |
1 |
0 |
Table 4-3 Summary of Exceedances for I-1
|
Parameter |
Action
Level Exceedance |
Limit
Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
One record on 31 Dec 2010 |
Two records on 6 and 24
Dec 2010 |
|
Total |
1 |
2 |
Table 4-4 Summary of Exceedances for I-2
Parameter |
Action
Level Exceedance |
Limit
Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
Nil |
One record on 24 Dec 2010 |
|
Total |
0 |
1 |
Table 4-5 Summary of Exceedances for I-3
Parameter |
Action
Level Exceedance |
Limit
Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
Two records on 3 and 22
Dec 2010 |
Three records on 1, 15
and 29 Dec 2010 |
|
Total |
2 |
3 |
Table 4-6 Summary of Exceedances for O-1(FT)
Parameter |
Action
Level Exceedance |
Limit
Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
One record on 24 Dec 2010 |
Three records on 13, 15
and 29 Dec 2010 |
|
Total |
1 |
3 |
Table 4-7 Summary of Exceedances for O-1(ET)
4.3.2
Results of measured water quality parameters during the reporting month
are shown in Table 4-8. Detailed results
including weather conditions and graphical presentations are enclosed in
Appendix I.
River Water Quality Monitoring
4.3.3
Five non-project
related exceedances were recorded for the river water quality monitoring within
the reporting month.
Exceedances of Suspended Solids Level
Action
Level at I-1 on 1 December 2010
4.3.4
An
exceedance of SS Action Level was recorded at I-1 on 1 December 2010. The
measured SS level (2.70 mg/L) was below the baseline Action / Limit Level and
was within the range of baseline SS concentration (1 – 10.5 mg/L). It was higher than the SS level measured at
upstream control station I-1-C (2.20 mg/L). General site cleaning and
housekeeping, rebar fixing at Bay 23, formwork at Bay 23, horizontal drilling
and GI monitoring were undertaken during measurement. No direct disturbance was observed from the
site. Thus, the exceedance was
considered to be contributed by natural variation and no action was required.
Limit
Level at I-2 on 6 December 2010
4.3.5
An
exceedance of SS Limit Level was recorded at I-2 on 6 December 2010 The measured
SS level (3.20 mg/L) was below baseline Action / Limit Level and within the
range of baseline SS concentration (1 - 8.5 mg/L) but was more than 130% of the
SS level measured at the upstream control station (I-2-C)(2.00 mg/L). General
site cleaning and housekeeping, excavation (drilling holes) at vortex drop
shaft, excavation (drilling holes) at man access shaft, rock breaking for
jacking pipe at Portion G and erection of 60 ton temporary steel platform at
Portion G were undertaken during measurement.
No direct disturbance was observed from the site. Thus, the exceedance was considered to be
contributed by natural variation and no action was required.
Limit Level at I-2 on 24 December 2010
4.3.6
An
exceedance of SS Limit Level was recorded at I-2 on 24 December 2010. The
measured SS level (3.05 mg/L) was below baseline Action / Limit Level and
within the range of baseline SS concentration (1 - 8.5 mg/L) but was more than
130% of the SS level measured at the upstream control station (I-2-C) (2.10
mg/L). General site cleaning and housekeeping, excavation (drilling holes) at
vortex drop shaft and excavation (drilling holes) at man access shaft, rock
breaking for 16th jacking pipe at Portion G, erection of 60 ton
temporary steel platform at Portion G and excavation for 750 step channel (SC)
and catchpit were undertaken during measurement. No direct disturbance was observed from the
site. Thus, the exceedance was considered to be contributed by natural
variation and no action was required.
Limit Level at I-3 on 24 December 2010
4.3.7
An
exceedance of SS Limit Level was recorded at I-3 on 24 December 2010. The
measured SS level (4.15 mg/L) was below baseline Action / Limit Level and
within the range of baseline SS concentration (1 - 7.5 mg/L) but was more than
130% of the SS level measured at the upstream control station (I-3-C) (2.00
mg/L). General site cleaning and housekeeping, PB wall H-pile extension,
approach channel extension, and shaft excavation were undertaken during
measurement. No direct disturbance was
observed from the site. Thus, the
exceedance was considered to be contributed by natural variation and no action
was required.
Action
Level at I-2 on 31 December 2010
4.3.8
An
exceedance of SS Action Level was recorded at I-2 on 31 December 2010. The measured SS level (2.45 mg/L) was below baseline Action / Limit Level and within the
range of baseline SS concentration (1 - 8.5 mg/L) but was more than 120% of the
SS level measured at the upstream control station (I-2-C) (2.00 mg/L). General site cleaning, housekeeping and temporary traffic
arrangement (TTA), excavation (drilling holes) at vortex drop shaft, excavation
(drilling holes and rock spilling) at man access shaft, closed formwork for dry
flow channel, rock breaking for 16th jacking pipe at Portion G,
erection of 60 ton temporary steel platform at Portion G and excavation for 750
SC and catchpit were undertaken during measurement. No direct disturbance was
observed from the site. Thus, the exceedance was considered to be contributed
by natural variation and no action was required.
Marine Water Quality
Monitoring
4.3.9
Nine non-project related exceedances were recorded for
the marine water quality monitoring within the reporting month.
Exceedances of Suspended
Solids Level
Action
Level at O-1(FT) on 3 and 22 December 2010
4.3.10
Two exceedances of SS
Action Level were recorded on 3 and 22 December 2010 at O-1(FT). The
measured SS levels (7.38 and 12.95 mg/L respectively) were below the baseline
Action/Limit Level but was higher than 120% of the control station's SS level
(O-1-C(FT)) (6.13 and 10.40 mg/L respectively) at the same tide of the same
day. Only rock removal at Portion E on 3
December 2010 and amour rock removal from the sea wall to the derrick barge at
Portion E on 22 December 2010 were undertaken during measurement. Silt curtains had been provided
along Portion E boundary line and extended from seawater level to the bottom of
seabed during the marine works. Frame / floating
type silt curtains had also been employed at the derrick barge, and rock
removal operation was confined in the inner (frame / floating type) silt
curtain. As such, the exceedances were considered to be contributed by natural
variation and no further action was required.
Limit Level at O-1(FT) on 1, 15 and 29
December 2010
4.3.11
Three exceedances of
SS Limit Level were recorded on 1, 15 and 29 December 2010 at O-1(FT). The
measured SS levels (varied from 3.20 to 7.83 mg/L) were below the baseline
Action / Limit Level but higher than 130%
of the control station's SS level (O-1-C(FT)) (varied from 2.37 to 5.28 mg/L)
at the same tide of the same day. Only rock-fill removal from sea bed was
undertaken on 1 December 2010 and no marine dredging activities were undertaken
on 15 and 29 December 2010. As silt curtains were provided along Portion E
boundary line and extended from seawater level to the bottom of seabed, frame /
floating type silt curtains were deployed at the derrick barge, and dredging /
rock removal operation were confined in the inner (frame / floating type) silt
curtain. As such, the exceedances were
considered to be contributed by natural variation and no further action was
required.
Action
Level at O-1(ET) on 24 December 2010
4.3.12
An exceedance of SS Action Level was recorded on 24 December 2010. The
measured SS level (depth-averaged) (9.82 mg/L) at O-1(ET) was below the
baseline Action/Limit Level but higher than 120% of the control station's SS
level (O-1-C(ET)) (7.87 mg/L) at the same tide of the same day. No marine works
was undertaken during measurement. As
silt curtains had been deployed along the dredging boundary line and extended
from the seawater level to the seabed and floating type silt curtain had been
employed at the inner side, the exceedance was considered to be contributed by
natural variation and no further action was required.
Limit
Level at O-1(ET) on 13, 15 and 29 December 2010
4.3.13
Three exceedances of SS Limit Level were recorded on 13, 15 and 29
December 2010. The measured SS levels (depth-averaged) (9.20, 5.53 and 9.07 mg/L
respectively) were below the baseline Action and Limit Level but higher than
130% of the control station's SS level (O-1-C(ET)) (5.18, 3.97 and 6.03 mg/L
respectively) at the same tide of the same day. No marine works were undertaken
on 13, 15 and 29 December 2010. As such, the exceedances were considered to be
contributed by natural variation and no further action was required.
|
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 |
01-Dec-10 |
23.50 |
7.01 |
3.42 / 3.34 |
7.92 |
3.21 |
9.75 / 12.47 |
2.70 |
8.85 / 10.17 |
|
|
03-Dec-10 |
22.70 |
7.71 |
|
7.95 |
3.48 |
|
2.50 |
|
|
|
06-Dec-10 |
25.00 |
6.99 |
|
7.96 |
6.39 |
|
4.25 |
|
|
|
08-Dec-10 |
21.70 |
7.22 |
|
7.98 |
5.10 |
|
4.30 |
|
|
|
10-Dec-10 |
21.70 |
7.05 |
|
8.06 |
4.76 |
|
4.15 |
|
|
|
13-Dec-10 |
21.50 |
6.95 |
|
8.02 |
5.60 |
|
4.65 |
|
|
|
15-Dec-10 |
21.20 |
7.11 |
|
7.98 |
6.59 |
|
2.75 |
|
|
|
17-Dec-10 |
17.20 |
7.58 |
|
8.08 |
6.68 |
|
2.00 |
|
|
|
20-Dec-10 |
21.70 |
7.37 |
|
8.05 |
3.12 |
|
2.00 |
|
|
|
22-Dec-10 |
21.55 |
6.97 |
|
8.14 |
2.98 |
|
2.00 |
|
|
|
24-Dec-10 |
20.10 |
7.19 |
|
8.09 |
4.39 |
|
2.00 |
|
|
|
29-Dec-10 |
18.60 |
7.62 |
|
8.91 |
2.39 |
|
2.00 |
|
|
|
31-Dec-10 |
18.80 |
7.32 |
|
8.09 |
3.23 |
|
2.00 |
|
Note: Italic indicates
the occurrence of exceedance of Action level.
Bold
indicates the occurrence of exceedance of Limit level.
|
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 |
01-Dec-10 |
23.30 |
7.25 |
- / - |
7.90 |
3.42 |
- / - |
2.20 |
- / - |
|
|
03-Dec-10 |
22.50 |
7.64 |
|
7.96 |
3.67 |
|
2.60 |
|
|
|
06-Dec-10 |
25.00 |
7.14 |
|
7.95 |
6.48 |
|
5.15 |
|
|
|
08-Dec-10 |
21.80 |
7.37 |
|
8.01 |
5.21 |
|
3.80 |
|
|
|
10-Dec-10 |
21.50 |
7.36 |
|
8.07 |
4.82 |
|
3.80 |
|
|
|
13-Dec-10 |
21.20 |
7.21 |
|
8.03 |
5.82 |
|
5.20 |
|
|
|
15-Dec-10 |
21.00 |
7.34 |
|
7.96 |
6.81 |
|
4.05 |
|
|
|
17-Dec-10 |
17.40 |
8.50 |
|
8.10 |
6.80 |
|
2.00 |
|
|
|
20-Dec-10 |
21.60 |
7.50 |
|
8.03 |
3.23 |
|
2.30 |
|
|
|
22-Dec-10 |
21.20 |
7.18 |
|
8.15 |
3.12 |
|
2.10 |
|
|
|
24-Dec-10 |
20.00 |
7.48 |
|
8.10 |
4.46 |
|
2.00 |
|
|
|
29-Dec-10 |
18.80 |
7.86 |
|
8.90 |
2.48 |
|
2.00 |
|
|
|
31-Dec-10 |
18.80 |
7.24 |
|
8.10 |
3.22 |
|
2.00 |
|
Note: Italic indicates
the occurrence of exceedance of Action level.
Bold
indicates the occurrence of exceedance of Limit level.
|
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 |
01-Dec-10 |
23.40 |
7.23 |
3.66
/ 3.63 |
7.96 |
1.54 |
6.63
/ 6.99 |
2.00 |
7.68
/ 8.34 |
|
|
03-Dec-10 |
22.70 |
7.47 |
|
7.91 |
1.70 |
|
2.00 |
|
|
|
06-Dec-10 |
24.90 |
6.78 |
|
7.97 |
1.86 |
|
3.20 |
|
|
|
08-Dec-10 |
21.50 |
7.10 |
|
8.02 |
1.80 |
|
2.00 |
|
|
|
10-Dec-10 |
21.45 |
6.91 |
|
8.03 |
1.32 |
|
2.00 |
|
|
|
13-Dec-10 |
21.00 |
7.14 |
|
8.01 |
1.70 |
|
2.00 |
|
|
|
15-Dec-10 |
21.00 |
7.27 |
|
7.96 |
2.38 |
|
2.00 |
|
|
|
17-Dec-10 |
17.00 |
7.71 |
|
8.04 |
1.84 |
|
2.00 |
|
|
|
20-Dec-10 |
21.50 |
7.16 |
|
8.05 |
2.12 |
|
2.00 |
|
|
|
22-Dec-10 |
21.50 |
7.20 |
|
8.15 |
1.99 |
|
2.20 |
|
|
|
24-Dec-10 |
20.00 |
7.54 |
|
8.10 |
1.59 |
|
3.05 |
|
|
|
29-Dec-10 |
18.90 |
7.62 |
|
8.87 |
3.02 |
|
2.00 |
|
|
|
31-Dec-10 |
19.20 |
7.44 |
|
8.08 |
2.52 |
|
2.45 |
|
Note: Italic indicates
the occurrence of exceedance of Action level.
Bold
indicates the occurrence of exceedance of Limit level.
|
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 |
01-Dec-10 |
23.30 |
6.84 |
- / - |
7.92 |
1.57 |
- / - |
3.15 |
- / - |
|
|
03-Dec-10 |
22.55 |
7.42 |
|
7.98 |
1.68 |
|
2.00 |
|
|
|
06-Dec-10 |
25.20 |
6.85 |
|
7.95 |
1.85 |
|
2.00 |
|
|
|
08-Dec-10 |
21.80 |
7.19 |
|
8.01 |
1.86 |
|
2.00 |
|
|
|
10-Dec-10 |
21.20 |
7.15 |
|
8.02 |
1.32 |
|
2.05 |
|
|
|
13-Dec-10 |
21.10 |
6.98 |
|
8.00 |
1.76 |
|
2.00 |
|
|
|
15-Dec-10 |
21.20 |
7.30 |
|
7.99 |
2.51 |
|
11.20 |
|
|
|
17-Dec-10 |
17.10 |
7.97 |
|
8.06 |
1.92 |
|
2.00 |
|
|
|
20-Dec-10 |
21.90 |
7.32 |
|
8.06 |
2.21 |
|
2.00 |
|
|
|
22-Dec-10 |
21.30 |
7.31 |
|
8.13 |
1.94 |
|
3.55 |
|
|
|
24-Dec-10 |
20.20 |
7.32 |
|
8.08 |
1.74 |
|
2.10 |
|
|
|
29-Dec-10 |
18.90 |
8.27 |
|
8.88 |
3.68 |
|
2.00 |
|
|
|
31-Dec-10 |
19.00 |
7.56 |
|
8.06 |
2.62 |
|
2.00 |
|
Note: Italic indicates
the occurrence of exceedance of Action level.
Bold
indicates the occurrence of exceedance of Limit level.
|
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 |
01-Dec-10 |
23.60 |
7.03 |
3.65 / 3.51 |
7.99 |
1.90 |
3.99 / 4.18 |
2.00 |
6.13 / 7.23 |
|
|
03-Dec-10 |
22.70 |
7.54 |
|
8.00 |
2.89 |
|
2.20 |
|
|
|
06-Dec-10 |
25.20 |
6.81 |
|
7.98 |
1.88 |
|
2.00 |
|
|
|
08-Dec-10 |
22.00 |
6.94 |
|
7.97 |
2.03 |
|
2.00 |
|
|
|
10-Dec-10 |
21.60 |
6.89 |
|
8.02 |
1.85 |
|
2.25 |
|
|
|
13-Dec-10 |
21.40 |
6.98 |
|
8.00 |
1.98 |
|
2.00 |
|
|
|
15-Dec-10 |
20.90 |
7.28 |
|
8.01 |
2.28 |
|
2.00 |
|
|
|
17-Dec-10 |
17.00 |
7.33 |
|
8.10 |
1.92 |
|
2.00 |
|
|
|
20-Dec-10 |
21.60 |
7.38 |
|
8.06 |
2.28 |
|
2.00 |
|
|
|
22-Dec-10 |
21.20 |
6.97 |
|
8.19 |
1.80 |
|
2.00 |
|
|
|
24-Dec-10 |
20.20 |
7.32 |
|
8.07 |
1.68 |
|
4.15 |
|
|
|
29-Dec-10 |
18.80 |
7.48 |
|
8.90 |
1.45 |
|
2.00 |
|
|
|
31-Dec-10 |
19.00 |
7.28 |
|
8.08 |
1.83 |
|
2.00 |
|
Note: Italic indicates
the occurrence of exceedance of Action level.
Bold
indicates the occurrence of exceedance of Limit level.
|
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 |
01-Dec-10 |
23.70 |
7.26 |
- / - |
7.97 |
1.88 |
- / - |
2.00 |
- / - |
|
|
03-Dec-10 |
22.80 |
7.70 |
|
8.00 |
2.89 |
|
2.00 |
|
|
|
06-Dec-10 |
25.10 |
6.78 |
|
7.99 |
1.95 |
|
2.00 |
|
|
|
08-Dec-10 |
21.70 |
6.88 |
|
7.96 |
2.08 |
|
2.00 |
|
|
|
10-Dec-10 |
21.30 |
7.04 |
|
8.04 |
1.89 |
|
2.20 |
|
|
|
13-Dec-10 |
21.60 |
7.05 |
|
8.00 |
2.01 |
|
2.00 |
|
|
|
15-Dec-10 |
21.30 |
7.16 |
|
8.00 |
2.30 |
|
2.00 |
|
|
|
17-Dec-10 |
16.90 |
7.62 |
|
8.05 |
2.01 |
|
2.00 |
|
|
|
20-Dec-10 |
21.80 |
7.24 |
|
8.08 |
2.17 |
|
2.00 |
|
|
|
22-Dec-10 |
21.50 |
7.11 |
|
8.16 |
1.90 |
|
2.00 |
|
|
|
24-Dec-10 |
20.40 |
7.77 |
|
8.06 |
1.71 |
|
2.00 |
|
|
|
29-Dec-10 |
19.00 |
7.56 |
|
8.91 |
1.47 |
|
2.00 |
|
|
|
31-Dec-10 |
19.00 |
7.53 |
|
8.08 |
1.88 |
|
2.00 |
|
Note: Italic indicates the
occurrence of exceedance of Action level.
Bold indicates
the occurrence of exceedance of Limit level.
|
Station |
Date |
Depth |
Temperature (℃) (depth-averaged) |
DO (mg/L) |
Action / Limit Level for DO (mg/L) |
pH (depth-averaged) |
Turbidity (NTU) (depth-averaged) |
Action / Limit Level for Turbidity (NTU) |
SS (mg/L) (depth-averaged) |
Action / Limit Level for SS (mg/L) |
|
O-1(FT) |
01-Dec-10 |
Surface |
22.95 |
7.28 |
6.84 / 6.81 |
8.27 |
4.15 |
10.35 / 13.15 |
7.83 |
14.1 / 18.08 |
|
|
|
Middle |
7.17 |
|
|
|||||
|
|
|
Bottom |
7.15 |
6.99 / 6.96 |
|
|
||||
|
|
03-Dec-10 |
Surface |
22.70 |
7.23 |
6.84 / 6.81 |
8.19 |
3.92 |
|
7.38 |
|
|
|
|
Middle |
7.43 |
|
|
|||||
|
|
|
Bottom |
7.16 |
6.99 / 6.96 |
|
|
||||
|
|
06-Dec-10 |
Surface |
23.70 |
7.23 |
6.84 / 6.81 |
8.32 |
8.26 |
|
10.60 |
|
|
|
|
Middle |
7.04 |
|
|
|||||
|
|
|
Bottom |
7.17 |
6.99 / 6.96 |
|
|
||||
|
|
08-Dec-10 |
Surface |
21.73 |
7.32 |
6.84 / 6.81 |
8.31 |
8.67 |
|
9.68 |
|
|
|
|
Middle |
7.13 |
|
|
|||||
|
|
|
Bottom |
7.21 |
6.99 / 6.96 |
|
|
||||
|
|
10-Dec-10 |
Surface |
21.77 |
7.20 |
6.84 / 6.81 |
8.28 |
6.78 |
|
4.70 |
|
|
|
|
Middle |
7.12 |
|
|
|||||
|
|
|
Bottom |
7.40 |
6.99 / 6.96 |
|
|
||||
|
|
13-Dec-10 |
Surface |
21.50 |
7.09 |
6.84 / 6.81 |
8.29 |
7.19 |
|
7.83 |
|
|
|
|
Middle |
7.22 |
|
|
|||||
|
|
|
Bottom |
7.42 |
6.99 / 6.96 |
|
|
||||
|
|
15-Dec-10 |
Surface |
21.00 |
7.19 |
6.84 / 6.81 |
8.30 |
3.87 |
|
5.82 |
|
|
|
|
Middle |
7.27 |
|
|
|||||
|
|
|
Bottom |
7.22 |
6.99 / 6.96 |
|
|
Note: Italic indicates the
occurrence of exceedance of Action level.
Bold indicates
the occurrence of exceedance of Limit level.
|
Station |
Date |
Depth |
Temperature (℃) (depth-averaged) |
DO (mg/L) |
Action / Limit Level for DO (mg/L) |
pH (depth-averaged) |
Turbidity (NTU) (depth-averaged) |
Action / Limit Level for Turbidity (NTU) |
SS (mg/L) (depth-averaged) |
Action / Limit Level for SS (mg/L) |
|
O-1(FT) |
17-Dec-10 |
Surface |
17.67 |
7.44 |
6.84 / 6.81 |
8.20 |
5.09 |
10.35 / 13.15 |
6.83 |
14.1 / 18.08 |
|
|
|
Middle |
7.48 |
|
|
|||||
|
|
|
Bottom |
7.89 |
6.99 / 6.96 |
|
|
||||
|
|
20-Dec-10 |
Surface |
21.80 |
7.36 |
6.84 / 6.81 |
8.29 |
3.18 |
|
2.67 |
|
|
|
|
Middle |
7.42 |
|
|
|||||
|
|
|
Bottom |
7.26 |
6.99 / 6.96 |
|
|
||||
|
|
22-Dec-10 |
Surface |
20.07 |
7.63 |
6.84 / 6.81 |
8.31 |
8.24 |
|
12.95 |
|
|
|
|
Middle |
7.42 |
|
|
|||||
|
|
|
Bottom |
7.36 |
6.99 / 6.96 |
|
|
||||
|
|
24-Dec-10 |
Surface |
20.23 |
7.50 |
6.84 / 6.81 |
8.09 |
7.68 |
|
9.45 |
|
|
|
|
Middle |
7.48 |
|
|
|||||
|
|
|
Bottom |
7.55 |
6.99 / 6.96 |
|
|
||||
|
|
29-Dec-10 |
Surface |
20.10 |
7.39 |
6.84 / 6.81 |
8.18 |
3.41 |
|
3.20 |
|
|
|
|
Middle |
7.44 |
|
|
|||||
|
|
|
Bottom |
7.51 |
6.99 / 6.96 |
|
|
||||
|
|
31-Dec-10 |
Surface |
19.20 |
7.40 |
6.84 / 6.81 |
8.26 |
4.80 |
|
5.68 |
|
|
|
|
Middle |
7.37 |
|
|
|||||
|
|
|
Bottom |
7.65 |
6.99 / 6.96 |
|
|
Note: Italic indicates the occurrence of
exceedance of Action level.
Bold indicates
the occurrence of exceedance of Limit level.
|
Station |
Date |
Depth |
Temperature (℃) (depth-averaged) |
DO (mg/L) |
Action / Limit Level for DO (mg/L) |
pH (depth-averaged) |
Turbidity (NTU) (depth-averaged) |
Action / Limit Level for Turbidity (NTU) |
SS (mg/L) (depth-averaged) |
Action / Limit Level for SS (mg/L) |
|
O-1-C(FT) |
01-Dec-10 |
Surface |
22.83 |
7.25 |
-
/ - |
8.27 |
3.94 |
- / - |
5.28 |
- / - |
|
|
|
Middle |
7.12 |
|
|
|||||
|
|
|
Bottom |
7.03 |
-
/ - |
|
|
||||
|
|
03-Dec-10 |
Surface |
22.63 |
7.40 |
-
/ - |
8.19 |
3.78 |
|
6.13 |
|
|
|
|
Middle |
7.12 |
|
|
|||||
|
|
|
Bottom |
7.44 |
-
/ - |
|
|
||||
|
|
06-Dec-10 |
Surface |
23.65 |
7.18 |
-
/ - |
8.33 |
8.42 |
|
10.63 |
|
|
|
|
Middle |
7.33 |
|
|
|||||
|
|
|
Bottom |
7.08 |
-
/ - |
|
|
||||
|
|
08-Dec-10 |
Surface |
21.68 |
7.24 |
-
/ - |
8.31 |
9.63 |
|
11.27 |
|
|
|
|
Middle |
7.43 |
|
|
|||||
|
|
|
Bottom |
7.11 |
-
/ - |
|
|
||||
|
|
10-Dec-10 |
Surface |
21.70 |
7.24 |
-
/ - |
8.28 |
7.59 |
|
6.13 |
|
|
|
|
Middle |
7.16 |
|
|
|||||
|
|
|
Bottom |
7.29 |
-
/ - |
|
|
||||
|
|
13-Dec-10 |
Surface |
21.38 |
7.33 |
-
/ - |
8.30 |
8.78 |
|
12.57 |
|
|
|
|
Middle |
7.19 |
|
|
|||||
|
|
|
Bottom |
7.26 |
-
/ - |
|
|
||||
|
|
15-Dec-10 |
Surface |
21.00 |
7.31 |
-
/ - |
8.30 |
3.99 |
|
3.67 |
|
|
|
|
Middle |
7.28 |
|
|
|||||
|
|
|
Bottom |
7.17 |
-
/ - |
|
|
Note: Italic indicates the
occurrence of exceedance of Action level.
Bold indicates
the occurrence of exceedance of Limit level.
|
Station |
Date |
Depth |
Temperature (℃) (depth-averaged) |
DO (mg/L) |
Action / Limit Level for DO (mg/L) |
pH (depth-averaged) |
Turbidity (NTU) (depth-averaged) |
Action / Limit Level for Turbidity (NTU) |
SS (mg/L) (depth-averaged) |
Action / Limit Level for SS (mg/L) |
|
O-1-C(FT) |
17-Dec-10 |
Surface |
17.58 |
7.66 |
-
/ - |
8.21 |
5.34 |
- / - |
5.98 |
- / - |
|
|
|
Middle |
7.62 |
|
|
|||||
|
|
|
Bottom |
7.66 |
-
/ - |
|
|
||||
|
|
20-Dec-10 |
Surface |
21.78 |
7.25 |
-
/ - |
8.29 |
3.29 |
|
2.33 |
|
|
|
|
Middle |
7.38 |
|
|
|||||
|
|
|
Bottom |
7.20 |
-
/ - |
|
|
||||
|
|
22-Dec-10 |
Surface |
20.35 |
7.66 |
-
/ - |
8.30 |
8.37 |
|
10.40 |
|
|
|
|
Middle |
7.53 |
|
|
|||||
|
|
|
Bottom |
7.41 |
-
/ - |
|
|
||||
|
|
24-Dec-10 |
Surface |
20.18 |
7.67 |
-
/ - |
8.09 |
9.09 |
|
17.93 |
|
|
|
|
Middle |
7.56 |
|
|
|||||
|
|
|
Bottom |
7.50 |
-
/ - |
|
|
||||
|
|
29-Dec-10 |
Surface |
20.08 |
7.39 |
-
/ - |
8.16 |
3.64 |
|
2.37 |
|
|
|
|
Middle |
7.28 |
|
|
|||||
|
|
|
Bottom |
7.34 |
-
/ - |
|
|
||||
|
|
31-Dec-10 |
Surface |
19.18 |
7.54 |
-
/ - |
8.26 |
5.41 |
|
5.77 |
|
|
|
|
Middle |
7.45 |
|
|
|||||
|
|
|
Bottom |
7.40 |
-
/ - |
|
|
Note: Italic indicates the
occurrence of exceedance of Action level.
Bold indicates
the occurrence of exceedance of Limit level.
|
Station |
Date |
Depth |
Temperature (℃) (depth-averaged) |
DO (mg/L) |
Action / Limit Level for DO (mg/L) |
pH (depth-averaged) |
Turbidity (NTU) (depth-averaged) |
Action / Limit Level for Turbidity (NTU) |
SS (mg/L) (depth-averaged) |
Action / Limit Level for SS (mg/L) |
|
O-1(ET) |
01-Dec-10 |
Surface |
22.97 |
7.17 |
7.02 / 6.94 |
8.24 |
3.37 |
11.87/13.44 |
5.22 |
13.25/14.39 |
|
|
|
Middle |
7.31 |
|
|
|||||
|
|
|
Bottom |
7.19 |
6.7 / 6.48 |
|
|
||||
|
|
03-Dec-10 |
Surface |
22.25 |
7.55 |
7.02 / 6.94 |
8.19 |
2.92 |
|
6.93 |
|
|
|
|
Middle |
7.21 |
|
|
|||||
|
|
|
Bottom |
7.31 |
6.7 / 6.48 |
|
|
||||
|
|
06-Dec-10 |
Surface |
24.00 |
7.26 |
7.02 / 6.94 |
8.32 |
4.05 |
|
7.95 |
|
|
|
|
Middle |
7.32 |
|
|
|||||
|
|
|
Bottom |
7.12 |
6.7 / 6.48 |
|
|
||||
|
|
08-Dec-10 |
Surface |
21.98 |
7.30 |
7.02 / 6.94 |
8.31 |
5.74 |
|
5.80 |
|
|
|
|
Middle |
7.16 |
|
|
|||||
|
|
|
Bottom |
7.30 |
6.7 / 6.48 |
|
|
||||
|
|
10-Dec-10 |
Surface |
22.17 |
7.14 |
7.02 / 6.94 |
8.30 |
5.07 |
|
5.67 |
|
|
|
|
Middle |
7.31 |
|
|
|||||
|
|
|
Bottom |
7.33 |
6.7 / 6.48 |
|
|
||||
|
|
13-Dec-10 |
Surface |
21.45 |
7.29 |
7.02 / 6.94 |
8.30 |
6.24 |
|
9.20 |
|
|
|
|
Middle |
7.14 |
|
|
|||||
|
|
|
Bottom |
7.09 |
6.7 / 6.48 |
|
|
||||
|
|
15-Dec-10 |
Surface |
21.03 |
7.42 |
7.02 / 6.94 |
8.30 |
3.11 |
|
5.53 |
|
|
|
|
Middle |
7.50 |
|
|
|||||
|
|
|
Bottom |
7.35 |
6.7 / 6.48 |
|
|
Note: Italic indicates the
occurrence of exceedance of Action level.
Bold indicates
the occurrence of exceedance of Limit level.
|
Station |
Date |
Depth |
Temperature (℃) (depth-averaged) |
DO (mg/L) |
Action / Limit Level for DO (mg/L) |
pH (depth-averaged) |
Turbidity (NTU) (depth-averaged) |
Action / Limit Level for Turbidity (NTU) |
SS (mg/L) (depth-averaged) |
Action / Limit Level for SS (mg/L) |
|
O-1(ET) |
17-Dec-10 |
Surface |
17.45 |
7.72 |
7.02 / 6.94 |
8.21 |
5.99 |
11.87/13.44 |
5.28 |
13.25/14.39 |
|
|
|
Middle |
7.52 |
|
|
|||||
|
|
|
Bottom |
7.70 |
6.7 / 6.48 |
|
|
||||
|
|
20-Dec-10 |
Surface |
21.60 |
7.25 |
7.02 / 6.94 |
8.29 |
4.32 |
|
5.93 |
|
|
|
|
Middle |
7.38 |
|
|
|||||
|
|
|
Bottom |
7.38 |
6.7 / 6.48 |
|
|
||||
|
|
22-Dec-10 |
Surface |
20.33 |
7.56 |
7.02 / 6.94 |
8.31 |
5.06 |
|
5.07 |
|
|
|
|
Middle |
7.57 |
|
|
|||||
|
|
|
Bottom |
7.35 |
6.7 / 6.48 |
|
|
||||
|
|
24-Dec-10 |
Surface |
20.50 |
7.46 |
7.02 / 6.94 |
8.10 |
6.16 |
|
9.82 |
|
|
|
|
Middle |
7.59 |
|
|
|||||
|
|
|
Bottom |
7.37 |
6.7 / 6.48 |
|
|
||||
|
|
29-Dec-10 |
Surface |
20.13 |
7.43 |
7.02 / 6.94 |
8.19 |
5.85 |
|
9.07 |
|
|
|
|
Middle |
7.55 |
|
|
|||||
|
|
|
Bottom |
7.52 |
6.7 / 6.48 |
|
|
||||
|
|
31-Dec-10 |
Surface |
19.03 |
7.26 |
7.02 / 6.94 |
8.24 |
5.50 |
|
7.17 |
|
|
|
|
Middle |
7.49 |
|
|
|||||
|
|
|
Bottom |
7.46 |
6.7 / 6.48 |
|
|
Note: Italic indicates the
occurrence of exceedance of Action level.
Bold indicates
the occurrence of exceedance of Limit level.
|
Station |
Date |
Depth |
Temperature (℃) (depth-averaged) |
DO (mg/L) |
Action / Limit Level for DO (mg/L) |
pH (depth-averaged) |
Turbidity (NTU) (depth-averaged) |
Action / Limit Level for Turbidity (NTU) |
SS (mg/L) (depth-averaged) |
Action / Limit Level for SS (mg/L) |
|
O-1-C(ET) |
01-Dec-10 |
Surface |
22.83 |
7.13 |
-
/ - |
8.24 |
3.39 |
- / - |
9.72 |
- / - |
|
|
|
Middle |
7.05 |
|
|
|||||
|
|
|
Bottom |
7.09 |
-
/ - |
|
|
||||
|
|
03-Dec-10 |
Surface |
22.30 |
7.69 |
-
/ - |
8.19 |
3.10 |
|
8.08 |
|
|
|
|
Middle |
7.39 |
|
|
|||||
|
|
|
Bottom |
7.31 |
-
/ - |
|
|
||||
|
|
06-Dec-10 |
Surface |
23.87 |
7.13 |
-
/ - |
8.32 |
4.11 |
|
7.02 |
|
|
|
|
Middle |
7.20 |
|
|
|||||
|
|
|
Bottom |
7.10 |
-
/ - |
|
|
||||
|
|
08-Dec-10 |
Surface |
21.90 |
7.32 |
-
/ - |
8.32 |
6.55 |
|
5.58 |
|
|
|
|
Middle |
7.20 |
|
|
|||||
|
|
|
Bottom |
7.34 |
-
/ - |
|
|
||||
|
|
10-Dec-10 |
Surface |
22.07 |
7.22 |
-
/ - |
8.29 |
5.24 |
|
6.47 |
|
|
|
|
Middle |
7.50 |
|
|
|||||
|
|
|
Bottom |
7.40 |
-
/ - |
|
|
||||
|
|
13-Dec-10 |
Surface |
21.37 |
7.21 |
-
/ - |
8.30 |
6.42 |
|
5.18 |
|
|
|
|
Middle |
7.27 |
|
|
|||||
|
|
|
Bottom |
7.15 |
-
/ - |
|
|
||||
|
|
15-Dec-10 |
Surface |
21.00 |
7.34 |
-
/ - |
8.30 |
3.03 |
|
3.97 |
|
|
|
|
Middle |
7.26 |
|
|
|||||
|
|
|
Bottom |
7.34 |
-
/ - |
|
|
Note: Italic indicates the
occurrence of exceedance of Action level.
Bold indicates
the occurrence of exceedance of Limit level.
|
Station |
Date |
Depth |
Temperature (℃) (depth-averaged) |
DO (mg/L) |
Action / Limit Level for DO (mg/L) |
pH (depth-averaged) |
Turbidity (NTU) (depth-averaged) |
Action / Limit Level for Turbidity (NTU) |
SS (mg/L) (depth-averaged) |
Action / Limit Level for SS (mg/L) |
|
O-1-C(ET) |
17-Dec-10 |
Surface |
16.92 |
7.47 |
-
/ - |
8.21 |
6.31 |
- / - |
5.55 |
- / - |
|
|
|
Middle |
7.76 |
|
|
|||||
|
|
|
Bottom |
7.57 |
-
/ - |
|
|
||||
|
|
20-Dec-10 |
Surface |
21.53 |
7.15 |
-
/ - |
8.30 |
5.58 |
|
6.08 |
|
|
|
|
Middle |
7.48 |
|
|
|||||
|
|
|
Bottom |
7.59 |
-
/ - |
|
|
||||
|
|
22-Dec-10 |
Surface |
20.25 |
7.42 |
-
/ - |
8.30 |
5.21 |
|
5.60 |
|
|
|
|
Middle |
7.36 |
|
|
|||||
|
|
|
Bottom |
7.53 |
-
/ - |
|
|
||||
|
|
24-Dec-10 |
Surface |
20.42 |
7.38 |
-
/ - |
3.97 |
7.19 |
|
7.87 |
|
|
|
|
Middle |
7.43 |
|
|
|||||
|
|
|
Bottom |
7.35 |
-
/ - |
|
|
||||
|
|
29-Dec-10 |
Surface |
20.05 |
7.33 |
-
/ - |
8.19 |
5.99 |
|
6.03 |
|
|
|
|
Middle |
7.42 |
|
|
|||||
|
|
|
Bottom |
7.32 |
-
/ - |
|
|
||||
|
|
31-Dec-10 |
Surface |
19.02 |
7.30 |
-
/ - |
8.24 |
6.06 |
|
8.62 |
|
|
|
|
Middle |
7.47 |
|
|
|||||
|
|
|
Bottom |
7.35 |
-
/ - |
|
|
Note: Italic indicates the
occurrence of exceedance of Action level.
Bold indicates
the occurrence of exceedance of Limit level.
Table 4-8 Water Quality Monitoring Results
4.4 DO, Temperature and pH Data Monitored on 1 December 2010
4.4.1 The previous calibration certificate for the multimeter
(for pH, temperature and DO measurements) was expired on 27 November 2010 and
the multimeter was recalibrated on 3 December 2010. Therefore, the water
quality data (pH, temperature and DO) collected on 1 December were not covered
under a valid calibration certificate of the multimeter. Although the
recalibration of the multimeter on 3 December 2010 indicated that the
multimeter was functioning normally within acceptable deviations, it is
considered that the water quality data (pH, temperature and DO) measured on 1
December 2010 should be considered for reference only.
Nevertheless, it is noted that the pH, temperature and DO data monitored at
various stations on 1 December 2010 are similar to the values measured on 3
December 2010. Effluent discharges from the construction sites at I-1,
I-2 and I-3 have been controlled under the wastewater discharge licenses.
Mitigation measures were deployed at various construction sites during
monitoring. These included: (1) silt curtains for marine works (rock
removal) at the marine basin of Outfall; (2) wastewater treatment plants at
I-1, I-2 and I-3; (3) diversion of existing streams that were bunded by sealed
concrete block walls at I-1, I-2 and I-3; and (4) bunded off the existing
stream by sand bag to prevent washing out of excavated material from the
working area at I-2. Thus, adverse water quality impact on DO at various
stations due to the Project on 1 December was not anticipated.
4.5 Turbidity Data Monitored on 24 December 2010
4.5.1 The previous calibration certificate for the turbidimeter
(serial no. 215619) was expired on 24 December 2010 and the turbidimeter was
recalibrated on 28 December 2010. Therefore, the turbidity data collected
on 24 December were not covered under a valid calibration certificate of the
turbidimeter. The recalibration of the turbidimeter on 28 December 2010
indicated that the turbidimeter was functioning normally within acceptable
deviations. However, the turbidity data measured on 24 December 2010 should be
considered for reference only.
4.5.2 As shown in Table 4.8, the turbidity levels measured at various control stations were higher than the turbidity level of the corresponding impact stations on 24 December 2010. Four-point on-site calibration of the turbidimeter was conducted before subsequent measurements and, thus, all measurements on 24 December 2010 were based on same calibration curve. The higher turbidity levels at control stations (where the water qualities were not affected by the project) and the relatively lower turbidity levels of the impact stations (where water qualities were or were not affected by the Project) showed that the Project did not contribute any significant adverse impact on the turbidity levels at the various impact monitoring stations.
4.5.3 In addition, effluent discharges from the construction sites at I-1, I-2 and I-3 have been controlled under the wastewater discharge licenses and mitigation measures were deployed at various construction sites during monitoring, including: (1) silt curtains for marine works (rock removal) at the marine basin of Outfall; (2) wastewater treatment plants at I-1, I-2 and I-3; and (3) diversion of existing streams that were bunded by sealed concrete block walls at I-1, I-2 and I-3, so the water quality of various locations are under sufficient protection. Therefore, adverse water quality impact on turbidity at various monitoring stations due to the Project on 24 December 2010 was not anticipated.
4.6 Summary of Project-Related Exceedances
4.6.1 Table 4-9 summarises the project-related exceedance results recorded in December 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 |
27 |
0 |
0 |
0 |
0 |
|
Water |
130 |
0 |
0 |
0 |
0 |
Table 4-9 Summary
of Project-Related Exceedances
5.1.1
The status of waste management is summarised in Table 5-1.
|
Status of waste management |
Quantity |
|
Inert C&D
Material Disposed of to Public Fill at Tuen Mun (m3) |
12,684.6 |
|
Inert C&D
Material Reused in this Contracts (m3) |
595.0 |
|
Inert C&D
Material Reused in other Contracts* (m3) |
4,955.0 |
|
Metals Generated (kg) |
18.0 |
|
Paper / Cardboard
Packaging (kg) |
400.0 |
|
Plastics (kg) |
20.0 |
|
Chemical Waste (kg) |
7,450.2 |
|
General Waste Disposed of to NENT
Landfill (m3) |
56.0 |
* Other Contract includes DC/2007/08,
YL/2009/01, HY/2007/10, DC/2007/17 and Wo Shang Wai.
Table
5-1 Waste Generated in December 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 |
|
2 December 2010 |
1.
Air compressor side panel cover was found
not properly installed at Intake I-3. |
1.
The Contractor was reminded to install the
side panel cover properly. |
1. The side panel cover was
installed properly on 4 December 2010. (Closed) |
|
2.
The emission noise label
was found not stuck properly on the air compressor at Intake I-3. |
2.
The Contractor was
reminded to stick the emission noise label at the air compressor properly. |
2. Noise emission label was stuck on the air compressor properly on 3 December
2010. (Closed) |
|
|
3.
Noise insulation wrapping
for rock breaker was found not installed properly at Intake I-3. |
3.
The Contractor was reminded
to apply noise insulation wrapping for the rock breaker properly. |
3. Noise insulation wrapping was applied on the rock breaker properly on
3 December 2010. (Closed) |
|
|
17 December 2010 |
1.
Stagnant water accumulated
on the tarpaulin was found at Castle Peak Road works area. |
1.
The Contractor was reminded to remove
accumulated water after each rainy day |
1.
Accumulated water was
removed on 17 December 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.
7.1.3
EPD received two public complaints regarding daytime construction
noise from outfall construction site on 17 November 2010. The complaints were about barge squeaking and
rock breaking. The ET have conducted
site inspection at the Outfall construction site and the Greenview Terrace (NSR
9) on 2 and 17 December 2010 to review and
audit the site setting, noise mitigation measures implemented on-site and the
environmental performance of the contractor. Enhanced on-site noise mitigation
measures have been implemented by the contractor. A noise investigation report
was submitted to the EPD on 24 December 2010. The issue of noise complaints was
considered closed. Details of the past complaint investigation and observations can
be referred to Appendix K.
7.1.4
Cumulative statistics of
environmental complaints are shown in Table 7-1.
|
Complaints Received in the
Reporting Month |
Cumulative Number of Complaints |
|
0 |
20 |
Table
7-1 Cumulative Statistics of Environmental Complaints
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 and conviction |
||
|
December 2010 |
Cumulative |
December 2010 |
Cumulative |
|
0 |
0 |
0 |
0 |
Table 8-1 Cumulative Statistics of Notification of Summons and Successful Prosecutions and Convictions
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;
·
TBM drilling of the tunnel and mucking out of tunnel spoil
at Outfall;
·
Drilling, excavation and rock splitting at spiral ramp at
Outfall;
·
Pre-bored H-pile drilling, excavation and soil nailing for
CPR box culvert construction at Outfall;
·
Removal of sea wall and amour rocks for basin scheme at
Outfall Portion E;
·
Installation of marine sea wall block and amour rock for
basin scheme at Portion E;
·
Construction of PB wall at I-3;
·
Erection of tower crane at I-3;
·
Drilling and excavation of vortex shaft at I-3;
·
Pipe jacking at Portion G at I-2;
·
Construction of retaining wall at I-2;
·
Pre-bored H-pile construction for skin wall at Portion G at
I-2;
·
Construction for skin wall at Portion G at I-2;
·
Drilling, excavation and rock splitting of man access shaft
and vortex drop shaft at I-2;
·
Construction of approach channel structure at I-2;
·
Cascade and channel modification concrete structure works at I-1;
·
Horizontal drilling at I-1; and
·
Backfilling of spiral ramp centre void at I-1.
|
|
|
|
|
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 |