



|
|
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 Air Borne Noise
Table 3‑8 Event/Action Plan for Airborne 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 Air Borne 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 November 2011
Table 6-1 Site Inspection
by ET
Table 7-1 Cumulative
Statistics of Environmental Complaints
|
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
l
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).
l
During the non restricted hours, major construction
activities undertaken by the Contractor at Tsuen Wan Drainage Tunnel included site cleaning and tidying at Outfall, I-1, I-2
and I-3; construction of spiral ramp structure at Outfall; tunnel boring
machine (TBM) drilling of the tunnel and mucking out of tunnel spoil at
Outfall; construction of box culvert and L-shaped retaining wall at
Outfall; trimming formation for precast slab at Portion E; installation of precast sea wall blocks at Portion E;
disposal of dredging materials to south of Cheung Chau at Portion E; disposal
of the excavated materials to TM38 at Portion E; drilling, rock splitting and
excavation of vortex shaft at I-3; drilling hole and excavation for main adit
tunnel at I-3; lowering down the permanent access road at PB wall at I-3; soil
nailing at the access road at I-3; river stream water diversion at I-3;
dismantling concrete bund wall and break the blinding layer at the approach
channel at I-3; blasting and excavation for upper part of man access adit for man
access shaft and deaeration chamber for vortex drop shaft at I-2; grouting
dowel bars and shotcreting at upper man access adit at I-2; excavation and soil
nailing works at L-shaped wall at I-2; construction of 1.5m diameter stepped
channel at I-2; construction of 300 U-channel and catchpit at Portion G at I-2;
removing formwork and curing for capping beam at Portion G at I-2; dismantling
steel platform (middle) at Portion G at I-2; reinstating concrete pavement next
to catchpit WS1 at I-2; drilling of H-pile and grouting at PA wall at I-1; weir
footing steel bar drilling and insert steel bars at nullah at I-1; and
backfilling tunnel spoil and place concrete platform at I-1.
l
Underground mining and probe drilling were
undertaken during the restricted hours in the reporting period.
l
As
confirmed by the Contractor, a total of 300 m3 dredging material was
disposed of to the south of Cheung Chau in November 2011.
l No exceedances have been
recorded for air quality monitoring during the reporting month.
l No exceedances have been recorded for noise
monitoring during the reporting month.
l
Exceedances for river water
quality monitoring are summarised in the
following table:
|
Parameter |
Action
Level Exceedance |
Limit
Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
One record at I-3 on 9 Nov 2011 |
Two records at I-1
on 9 Nov 2011 and at I-2 on 9 Nov 2011 |
|
SS |
Two records at I-1
on 2 Nov 2011 and at I-2 on 23 Nov 2011 |
Two records at I-1
on 9 Nov 2011 and at I-2 on 9 Nov 2011 |
l Exceedances for marine water quality monitoring
are summarised in the following table:
|
Parameter |
Action
Level Exceedance |
Limit
Level Exceedance |
|
DO |
One record at O-1(ET) on 4 Nov 2011 |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
Three records at O-1(FT)
on 23 and 28 Nov 2011, and at O-1(ET) on 2 Nov 2011 |
One record at
O-1(FT) on 7 Nov 2011 |
l The status of waste generation in the
reporting month is:
·
A total of
3,214.1 m
·
About 34.5
m3 general waste was disposed of to NENT Landfill;
·
About 400.0 kg paper/cardboard
was recycled in the reporting
month;
·
About 10.0 kg metal was
generated in the reporting month;
·
About 10.0 kg plastic waste
was disposed of in the reporting month; and
·
No chemical waste was
disposed of in the reporting month.
l
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.
l
As advised
by the Contractor and verified by ET:
·
No non-compliance
regarding the site inspection was received in the reporting month; and
·
No environmental complaint
was received during the reporting month.
·
No summons
and prosecution was received in the reporting month.
l
The major
construction works for the upcoming three months will be:
·
Site cleaning and tidying at
Outfall, I-1, I-2 and I-3;
·
TBM drilling of the tunnel and
mucking out of tunnel spoil at Outfall;
·
Construction of spiral ramp
structure at Outfall;
·
Construction of box culvert and
L-shaped retaining wall at Outfall;
·
Placing leveling stone for
formation of sea wall at Portion E;
·
Installation of precast panels
for construction of outfall apron at Portion E;
·
Drilling and excavation of vortex
shaft at I-3;
·
Reinstatement of slope at PB wall
at I-3;
·
Construction of approach channel
at I-3;
·
Blasting and excavation for man
access shaft and vortex drop shaft at I-2;
·
Construction of approach channel
structure at I-2;
·
Construction of drainage works at
Portion G at I-2; and
·
Preparation for TBM retrieval at I-1.
1.1.1
The
Drainage Services Department (DSD) proposed to construct a tunnel with an
internal diameter of 6.5 m and a length of 5.13 km, 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 designated 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
forty-fourth monthly EM&A report summarising the impact monitoring results
and audit findings of the EM&A programme in November 2011.
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
Outfall, I-1, I-2 and I-3;
l
Construction of spiral ramp
structure at Outfall;
l
Tunnel boring machine (TBM)
drilling of the tunnel and mucking out of tunnel spoil at Outfall;
l
Construction of box
culvert and L-shaped retaining wall at Outfall;
l
Trimming formation for precast
slab at Portion E;
l
Installation of precast sea wall blocks at Portion E;
l
Disposal of dredging materials to
south of Cheung Chau at Portion E;
l
Disposal of the excavated
materials to TM38 at Portion E;
l
Drilling, rock splitting and
excavation of vortex shaft at I-3;
l
Drilling hole and excavation for
main adit tunnel at I-3;
l
Lowering down the permanent
access road at PB wall at I-3;
l
Soil nailing at the access road
at I-3;
l
River stream water diversion at
I-3;
l
Dismantling concrete bund wall
and break the blinding layer at the approach channel at I-3;
l
Blasting and excavation for upper
part of man access adit for man access shaft and deaeration chamber for vortex
drop shaft at I-2;
l
Grouting dowel bars and
shotcreting at upper man access adit at I-2;
l
Excavation and soil nailing works
at L-shaped wall at I-2;
l
Construction of 1.5m diameter
stepped channel at I-2;
l
Construction of 300 U-channel and
catchpit at Portion G at I-2;
l
Removing formwork and curing for
capping beam at Portion G at I-2;
l
Dismantling steel platform
(middle) at Portion G at I-2;
l
Reinstating concrete pavement
next to catchpit WS1 at I-2;
l
Drilling of H-pile and grouting
at PA wall at I-1;
l
Weir footing steel bar drilling and
insert steel bars at nullah at I-1; and
l Backfilling
tunnel spoil and place concrete platform at I-1.
2.2.3
As confirmed by the Contractor, a total of 300 m3 dredging
material was disposed of to the south of Cheung Chau in November 2011.
2.2.4
Underground
mining and probe drilling were undertaken during the restricted hours in the
reporting period.
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
quality 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 are 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 and presented
to the nearest 0.1 dB(A) 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(30
min), L10 and L90 were measured throughout the
impact monitoring. An average, by sound
power, of six consecutive 5-minute 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 3 dB(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
equipment 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 facade
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 July 2009) 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
3.2.8
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 Air Borne 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 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. |
· 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 Airborne 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 near the Project site, it is suggested that a
programme of monitoring should be established to confirm the effectiveness of
these mitigation measures in 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 |
|
DO / Temperature
Meter |
YSI |
55/12 |
1 |
|
DO / Temperature/ pH
Meter |
YSI |
Professional Plus |
1 |
|
pH Meter |
Hanna |
HI-8014 |
1 |
|
Turbidimeter |
EUTECH |
TN-100 |
1 |
Table 3‑9 Water Quality Monitoring Equipment
3.3.8
All in situ
monitoring equipment were checked and calibrated prior to use. They 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 control 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 O-1 during 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 these 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 4 mg/L
except 5 mg/L for Fish Culture Zone or 1%-ile
of baseline data for surface and middle layer Bottom 2 mg/L
or 1%-ile of baseline data for bottom layer |
|
SS in
mg/L (depth-averaged) |
95%-ile
of baseline data or 120% of 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 findings; · 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 findings; · 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 findings; · 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; · 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 findings; · 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; · 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-hour TSP level are shown
in Table 4-1. All measurements were
recorded and presented to the nearest 0.1 mg/m3
in this report. Detailed 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-Nov-11 |
80.5 |
307/500 |
|
107.8 |
|||
|
88.0 |
|||
|
07-Nov-11 |
86.7 |
||
|
58.2 |
|||
|
68.1 |
|||
|
11-Nov-11 |
53.3 |
||
|
54.5 |
|||
|
80.5 |
|||
|
17-Nov-11 |
97.9 |
||
|
131.3 |
|||
|
73.1 |
|||
|
23-Nov-11 |
33.4 |
||
|
96.6 |
|||
|
37.2 |
|||
|
29-Nov-11 |
83.0 |
||
|
61.9 |
|||
|
38.4 |
|||
|
ASR 3 |
01-Nov-11 |
78.8 |
327/500 |
|
97.5 |
|||
|
85.0 |
|||
|
07-Nov-11 |
103.8 |
||
|
95.0 |
|||
|
72.5 |
|||
|
11-Nov-11 |
92.5 |
||
|
36.3 |
|||
|
72.5 |
|||
|
17-Nov-11 |
101.3 |
||
|
120.0 |
|||
|
111.3 |
|||
|
23-Nov-11 |
42.5 |
||
|
51.3 |
|||
|
67.5 |
|||
|
29-Nov-11 |
100.0 |
||
|
96.3 |
|||
|
62.5 |
|||
|
ASR 8 |
01-Nov-11 |
103.0 |
337/500 |
|
36.0 |
|||
|
149.3 |
|||
|
07-Nov-11 |
95.2 |
||
|
51.5 |
|||
|
81.1 |
|||
|
11-Nov-11 |
28.3 |
||
|
59.2 |
|||
|
57.9 |
|||
|
17-Nov-11 |
21.9 |
||
|
57.9 |
|||
|
66.9 |
|||
|
23-Nov-11 |
75.9 |
||
|
64.4 |
|||
|
84.9 |
|||
|
29-Nov-11 |
94.0 |
||
|
86.2 |
|||
|
42.5 |
|||
|
ASR 9 |
01-Nov-11 |
90.1 |
329/500 |
|
126.5 |
|||
|
71.3 |
|||
|
07-Nov-11 |
78.0 |
||
|
173.6 |
|||
|
48.4 |
|||
|
11-Nov-11 |
98.2 |
||
|
33.6 |
|||
|
78.0 |
|||
|
17-Nov-11 |
168.2 |
||
|
43.1 |
|||
|
24.2 |
|||
|
23-Nov-11 |
56.5 |
||
|
87.5 |
|||
|
57.9 |
|||
|
29-Nov-11 |
99.6 |
||
|
82.1 |
|||
|
57.9 |
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 air borne 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 and presented to the nearest 0.1 dB(A) 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-Nov-11 |
63.6 |
70 |
|
07-Nov-11 |
63.3 |
||
|
17-Nov-11 |
64.1 |
||
|
23-Nov-11 |
64.0 |
||
|
29-Nov-11 |
64.4 |
||
|
NSR 3 |
01-Nov-11 |
62.5 |
75 |
|
07-Nov-11 |
58.6 |
||
|
17-Nov-11 |
62.7 |
||
|
23-Nov-11 |
63.2 |
||
|
29-Nov-11 |
60.6 |
||
|
NSR 6 |
01-Nov-11 |
64.8 |
|
|
07-Nov-11 |
58.5 |
||
|
17-Nov-11 |
64.2 |
||
|
23-Nov-11 |
61.1 |
||
|
29-Nov-11 |
63.2 |
||
|
NSR 8 |
01-Nov-11 |
70.6 |
|
|
07-Nov-11 |
62.7 |
||
|
17-Nov-11 |
68.6 |
||
|
23-Nov-11 |
67.7 |
||
|
29-Nov-11 |
65.1 |
||
|
NSR 9 |
01-Nov-11 |
66.4 |
|
|
07-Nov-11 |
64.0 |
||
|
17-Nov-11 |
68.6 |
||
|
23-Nov-11 |
68.5 |
||
|
29-Nov-11 |
67.6 |
Table
4-2 Air
Borne Noise Monitoring Results
4.2.2
No project related noise exceedance
was recorded in 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 |
One
record on 9 Nov 2011 |
|
SS |
One
record on 2 Nov 2011 |
One
record on 9 Nov 2011 |
|
Total |
1 |
2 |
Table 4-3 Summary of Exceedances for I-1
|
Parameter |
Action
Level Exceedance |
Limit Level
Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
Nil |
One
record on 9 Nov 2011 |
|
SS |
One
record on 23 Nov 2011 |
One
record on 9 Nov 2011 |
|
Total |
1 |
2 |
Table 4-4 Summary of Exceedances for I-2
Parameter |
Action Level
Exceedance |
Limit
Level Exceedance |
|
DO |
Nil |
Nil |
|
Turbidity |
One
record on 9 Nov 2011 |
Nil |
|
SS |
Nil |
Nil |
|
Total |
1 |
0 |
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 23 and 28 Nov 2011 |
One
record on 7 Nov 2011 |
|
Total |
2 |
1 |
Table 4-6 Summary of Exceedances for O-1(FT)
Parameter |
Action Level
Exceedance |
Limit
Level Exceedance |
|
DO |
One record on 4 Nov 2011 |
Nil |
|
Turbidity |
Nil |
Nil |
|
SS |
One record on 2 Nov 2011 |
Nil |
|
Total |
2 |
0 |
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
Seven exceedances were recorded for the river water
quality monitoring within the reporting month.
Exceedances of Turbidity Level
Action
Level at I-3 on 9 November 2011
4.3.4
One exceedance of turbidity action level
was recorded at I-3 on 9 November 2011. The measured turbidity level (4.09 NTU)
was higher than the baseline action level, but lower than the turbidity level
(4.19 NTU) of the control station (I-3-C). Details of the construction
activities conducted on the monitoring days are given in Appendix J. No direct
disturbance was observed from the site. Therefore, the exceedance was
considered to be contributed by high turbidity level at upstream location.
Since the exceedance was non-project related, no further action was required.
Limit
Level at I-1 on 9 November 2011
4.3.5
One exceedance of turbidity limit
level was recorded at I-1 on 9 November 2011. The measured turbidity level
(15.06 NTU) was higher than the baseline limit level, but lower than the
turbidity level (15.42 NTU) of the control station (I-1-C). Details of the
construction activities conducted on the monitoring days are given in Appendix
J. No direct disturbance was observed from the site. About 44.2 mm rainfall was
recorded by the Hong Kong Observatory on the monitoring day. Therefore, the
exceedance was considered to be contributed by high turbidity level at upstream
location and rainfall. Since the exceedance was non-project related, no further
action was required.
Limit
Level at I-2 on 9 November 2011
4.3.6
One exceedance of turbidity limit
level was recorded at I-2 on 9 November 2011. The measured turbidity level
(19.50 NTU) was higher than the baseline limit level, but lower than 120% of
turbidity level (19.40 NTU) of the control station (I-2-C). Details of the
construction activities conducted on the monitoring days are given in Appendix
J. No direct disturbance was observed from the site. About 44.2 mm rainfall was
recorded by the Hong Kong Observatory on the monitoring day. Therefore, the
exceedance was considered to be contributed by high turbidity level at upstream
location and rainfall. Since the exceedance was non-project related, no further
action was required.
Exceedances of Suspended Solids Level
Action
Level at I-1 on 2 November 2011
4.3.7
One exceedance of SS action level
was recorded at I-1 on 2 November 2011. The measured SS level (7.05 mg/L) was
below the baseline action/limit level, but higher than 120% of the SS level
(5.60 mg/L) of the control station (I-1-C). Details of the construction activities
conducted on the monitoring day are given in Appendix J. No direct disturbance
was observed from the site. The exceedance was considered to be contributed by
natural variation and non-project related. Therefore, no further action was
required.
Action
Level at I-2 on 23 November 2011
4.3.8
One exceedance of SS action level
was recorded at I-2 on 23 November 2011. The measured SS level (2.60 mg/L) was
well below the baseline action/limit level and same as 130% of the SS level
(<2.00 mg/L) of the control station (I-2-C). Details of the construction
activities conducted on the monitoring day are given in Appendix J. No direct
disturbance was observed from the site. The exceedance was considered to be
contributed by natural variation and non-project related. Therefore, no further
action was required.
Limit
Level at I-1 on 9 November 2011
4.3.9
One exceedance of SS limit level was
recorded at I-1 on 9 November 2011. The measured SS level (12.70 mg/L) was
higher than the baseline limit level, but lower than the SS level (12.90 mg/L)
of the control station (I-1-C). Details of the construction activities
conducted on the monitoring day are given in Appendix J. No direct disturbance
was observed from the site. About 44.2 mm rainfall was recorded by the Hong
Kong Observatory on the monitoring day. Therefore, the exceedance was
considered to be contributed by high SS level at upstream location and
rainfall. Since the exceedance was non-project related, no further action was
required.
Limit
Level at I-2 on 9 November 2011
4.3.10
One exceedance of SS limit level was
recorded at I-2 on 9 November 2011. The
measured SS level (18.00 mg/L) was higher than the baseline limit level, but
lower than the SS level (18.20 mg/L) of the control station (I-2-C). Details of
the construction activities conducted on the monitoring day are given in
Appendix J. No direct disturbance was observed from the site. About 44.2 mm
rainfall was recorded by the Hong Kong Observatory on the monitoring day.
Therefore, the exceedance was considered to be contributed by high SS level at
upstream location and rainfall. Since the exceedance was non-project related,
no further action was required.
Marine Water Quality
Monitoring
4.3.11
Five exceedances were recorded for the marine water quality
monitoring within the reporting month.
Exceedances of Dissolved Oxygen Level
Action
Level at O-1(ET) (Marine Surface) on 4 November 2011
4.3.12
One exceedance of DO action level
was recorded at O-1(ET) (marine surface) on 4 November 2011. The measured DO level
(6.95 mg/L) at the monitoring station was below the baseline action level, but
higher than the DO level (6.91 mg/L) of the corresponding control station.
Details of the construction activities conducted on the monitoring day are
given in Appendix J. No direct disturbance was observed from the site. The
exceedance was considered to be contributed by natural variation and
non-project related. Therefore, no further action was required.
Exceedances of Suspended Solids Level
Action
Level at O-1(FT) on 23 and 28 November 2011
4.3.13
Two exceedances of SS action levels
were recorded at O-1(FT) on 23 and 28 November 2011. The measured SS levels
(5.97 and 8.33 mg/L, respectively) at the monitoring station were below the
baseline action/limit level, but higher than 120% of the SS level (4.78 and
6.42 mg/L, respectively) of the corresponding control station. Details of the
construction activities conducted on the monitoring days are given in Appendix
J. No direct disturbance was observed from the site. The exceedances were
considered to be contributed by natural variation and non-project related.
Therefore, no further action was required.
Action
Level at O-1(ET) on 2 November 2011
4.3.14
One exceedance of SS action level
was recorded at O-1(ET) on 2 November 2011. The measured SS level (9.23 mg/L)
at the monitoring station was below the baseline action/limit level, but higher
than 120% of the SS level (7.50 mg/L) of the corresponding control station.
Details of the construction activities conducted on the monitoring day are given
in Appendix J. No direct disturbance was
observed from the site. The exceedance was considered to be contributed by
natural variation and non-project related. Therefore, no further action was
required.
Limit
Level at O-1(FT) on 7 November 2011
4.3.15
One exceedance of SS action level
was recorded at O-1(FT) on 7 November 2011. The measured SS level (5.28 mg/L)
at the monitoring station was well below the baseline action/limit level, but
slightly higher than 130% of the SS level (3.87 mg/L) of the corresponding
control station. Details of the construction activities conducted on the
monitoring day are given in Appendix J. No direct disturbance was observed from
the site. The exceedance was considered to be contributed by natural variation
and non-project related. Therefore, 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 |
02-Nov-11 |
24.60 |
7.85 |
3.42 / 3.34 |
8.40 |
2.43 |
9.75 / 12.47 |
7.05 |
8.85 / 10.17 |
|
|
04-Nov-11 |
26.10 |
7.07 |
|
8.37 |
3.99 |
|
5.15 |
|
|
|
07-Nov-11 |
26.05 |
7.55 |
|
8.33 |
4.27 |
|
5.10 |
|
|
|
09-Nov-11 |
21.65 |
7.91 |
|
8.42 |
15.06 |
|
12.70 |
|
|
|
11-Nov-11 |
22.10 |
8.18 |
|
8.38 |
2.10 |
|
<2.00 |
|
|
|
14-Nov-11 |
26.70 |
7.45 |
|
8.40 |
3.50 |
|
<2.00 |
|
|
|
16-Nov-11 |
26.60 |
7.48 |
|
8.33 |
2.38 |
|
<2.00 |
|
|
|
18-Nov-11 |
26.10 |
7.50 |
|
8.37 |
3.35 |
|
3.05 |
|
|
|
21-Nov-11 |
22.70 |
7.82 |
|
8.16 |
3.68 |
|
2.25 |
|
|
|
23-Nov-11 |
22.00 |
8.40 |
|
8.25 |
2.50 |
|
<2.00 |
|
|
|
25-Nov-11 |
22.70 |
8.22 |
|
8.39 |
4.80 |
|
3.65 |
|
|
|
28-Nov-11 |
22.70 |
7.67 |
|
8.28 |
2.83 |
|
3.10 |
|
|
|
30-Nov-11 |
23.45 |
8.06 |
|
8.35 |
2.21 |
|
<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 |
02-Nov-11 |
24.55 |
7.93 |
- / - |
8.41 |
2.50 |
- / - |
5.60 |
- / - |
|
|
04-Nov-11 |
25.90 |
7.02 |
|
8.36 |
4.04 |
|
4.25 |
|
|
|
07-Nov-11 |
26.00 |
7.50 |
|
8.34 |
4.47 |
|
5.05 |
|
|
|
09-Nov-11 |
21.75 |
7.84 |
|
8.43 |
15.42 |
|
12.90
|
|
|
|
11-Nov-11 |
22.00 |
8.12 |
|
8.35 |
2.09 |
|
<2.00 |
|
|
|
14-Nov-11 |
26.50 |
7.55 |
|
8.41 |
3.65 |
|
<2.00 |
|
|
|
16-Nov-11 |
26.70 |
7.40 |
|
8.34 |
2.35 |
|
<2.00 |
|
|
|
18-Nov-11 |
26.00 |
7.57 |
|
8.38 |
3.41 |
|
2.75 |
|
|
|
21-Nov-11 |
22.80 |
7.82 |
|
8.16 |
3.79 |
|
<2.00 |
|
|
|
23-Nov-11 |
22.05 |
8.46 |
|
8.25 |
2.59 |
|
<2.00 |
|
|
|
25-Nov-11 |
22.65 |
8.25 |
|
8.38 |
5.01 |
|
4.90 |
|
|
|
28-Nov-11 |
22.70 |
7.78 |
|
8.28 |
2.90 |
|
2.80 |
|
|
|
30-Nov-11 |
23.40 |
8.13 |
|
8.36 |
2.32 |
|
<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 |
02-Nov-11 |
24.95 |
7.77 |
3.66 / 3.63 |
8.24 |
1.97 |
6.63 / 6.99 |
<2.00 |
7.68 / 8.34 |
|
|
04-Nov-11 |
26.00 |
6.97 |
|
8.31 |
2.13 |
|
<2.00 |
|
|
|
07-Nov-11 |
26.15 |
7.34 |
|
8.26 |
2.70 |
|
<2.00 |
|
|
|
09-Nov-11 |
21.55 |
7.86 |
|
8.40 |
19.50 |
|
18.00 |
|
|
|
11-Nov-11 |
22.80 |
8.23 |
|
8.41 |
2.38 |
|
<2.00 |
|
|
|
14-Nov-11 |
27.10 |
7.48 |
|
8.35 |
2.76 |
|
<2.00 |
|
|
|
16-Nov-11 |
26.65 |
7.43 |
|
8.40 |
2.11 |
|
<2.00 |
|
|
|
18-Nov-11 |
26.45 |
7.51 |
|
8.40 |
3.04 |
|
<2.00 |
|
|
|
21-Nov-11 |
23.25 |
8.02 |
|
8.07 |
2.68 |
|
<2.00 |
|
|
|
23-Nov-11 |
21.85 |
8.37 |
|
8.10 |
3.01 |
|
2.60 |
|
|
|
25-Nov-11 |
23.00 |
8.17 |
|
8.27 |
1.91 |
|
<2.00 |
|
|
|
28-Nov-11 |
23.00 |
7.84 |
|
8.19 |
1.95 |
|
<2.00 |
|
|
|
30-Nov-11 |
23.05 |
7.99 |
|
8.25 |
1.87 |
|
<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-C |
02-Nov-11 |
24.85 |
7.71 |
- / - |
8.23 |
2.01 |
- / - |
2.10 |
- / - |
|
|
04-Nov-11 |
26.15 |
6.89 |
|
8.30 |
2.32 |
|
<2.00 |
|
|
|
07-Nov-11 |
26.25 |
7.40 |
|
8.25 |
3.76 |
|
<2.00 |
|
|
|
09-Nov-11 |
21.50 |
7.80 |
|
8.40 |
19.40 |
|
18.20
|
|
|
|
11-Nov-11 |
22.70 |
8.33 |
|
8.42 |
2.40 |
|
<2.00 |
|
|
|
14-Nov-11 |
27.10 |
7.57 |
|
8.35 |
2.84 |
|
<2.00 |
|
|
|
16-Nov-11 |
26.80 |
7.56 |
|
8.41 |
2.25 |
|
<2.00 |
|
|
|
18-Nov-11 |
26.50 |
7.45 |
|
8.40 |
3.10 |
|
<2.00 |
|
|
|
21-Nov-11 |
23.50 |
8.07 |
|
8.07 |
2.79 |
|
<2.00 |
|
|
|
23-Nov-11 |
21.80 |
8.47 |
|
8.09 |
3.12 |
|
<2.00 |
|
|
|
25-Nov-11 |
22.90 |
8.22 |
|
8.26 |
1.92 |
|
<2.00 |
|
|
|
28-Nov-11 |
22.90 |
7.79 |
|
8.20 |
1.92 |
|
<2.00 |
|
|
|
30-Nov-11 |
23.00 |
8.05 |
|
8.25 |
1.89 |
|
<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 |
02-Nov-11 |
24.75 |
7.80 |
3.65 / 3.51 |
8.25 |
2.07 |
3.99 / 4.18 |
2.40 |
6.13 / 7.23 |
|
|
04-Nov-11 |
25.70 |
7.02 |
|
8.22 |
2.01 |
|
<2.00 |
|
|
|
07-Nov-11 |
26.45 |
7.37 |
|
8.38 |
2.29 |
|
<2.00 |
|
|
|
09-Nov-11 |
21.40 |
7.96 |
|
8.37 |
4.09 |
|
3.35 |
|
|
|
11-Nov-11 |
22.35 |
8.11 |
|
8.30 |
3.32 |
|
<2.00 |
|
|
|
14-Nov-11 |
26.80 |
7.49 |
|
8.34 |
2.15 |
|
<2.00 |
|
|
|
16-Nov-11 |
26.50 |
7.43 |
|
8.30 |
1.91 |
|
<2.00 |
|
|
|
18-Nov-11 |
23.50 |
7.94 |
|
8.20 |
2.82 |
|
<2.00 |
|
|
|
21-Nov-11 |
23.00 |
8.01 |
|
8.11 |
2.00 |
|
2.05 |
|
|
|
23-Nov-11 |
21.80 |
8.33 |
|
8.05 |
1.67 |
|
<2.00 |
|
|
|
25-Nov-11 |
22.80 |
8.29 |
|
8.18 |
1.89 |
|
<2.00 |
|
|
|
28-Nov-11 |
22.50 |
7.86 |
|
8.10 |
1.94 |
|
<2.00 |
|
|
|
30-Nov-11 |
22.90 |
8.07 |
|
8.22 |
2.10 |
|
<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 |
02-Nov-11 |
24.65 |
7.83 |
- / - |
8.28 |
2.06 |
- / - |
2.10 |
- / - |
|
|
04-Nov-11 |
25.80 |
6.97 |
|
8.22 |
2.03 |
|
<2.00 |
|
|
|
07-Nov-11 |
26.50 |
7.31 |
|
8.40 |
2.37 |
|
2.85 |
|
|
|
09-Nov-11 |
21.35 |
8.05 |
|
8.37 |
4.17 |
|
3.65 |
|
|
|
11-Nov-11 |
22.45 |
8.19 |
|
8.30 |
3.54 |
|
<2.00 |
|
|
|
14-Nov-11 |
26.95 |
7.54 |
|
8.34 |
2.17 |
|
<2.00 |
|
|
|
16-Nov-11 |
26.60 |
7.39 |
|
8.30 |
1.88 |
|
<2.00 |
|
|
|
18-Nov-11 |
23.55 |
8.00 |
|
8.22 |
2.75 |
|
2.40 |
|
|
|
21-Nov-11 |
23.00 |
7.95 |
|
8.10 |
2.05 |
|
2.10 |
|
|
|
23-Nov-11 |
21.90 |
8.36 |
|
8.04 |
1.68 |
|
<2.00 |
|
|
|
25-Nov-11 |
22.80 |
8.34 |
|
8.18 |
1.89 |
|
<2.00 |
|
|
|
28-Nov-11 |
22.60 |
7.90 |
|
8.10 |
1.91 |
|
<2.00 |
|
|
|
30-Nov-11 |
22.80 |
8.11 |
|
8.22 |
2.07 |
|
<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) |
02-Nov-11 |
Surface |
27.55 |
7.32 |
6.84 / 6.81 |
8.06 |
6.03 |
10.35 / 13.15 |
6.18 |
14.10 / 18.08 |
|
|
|
Middle |
7.30 |
|
|
|||||
|
|
|
Bottom |
7.21 |
6.99 / 6.96 |
|
|
||||
|
|
04-Nov-11 |
Surface |
27.90 |
7.01 |
6.84 / 6.81 |
8.10 |
3.42 |
|
5.02 |
|
|
|
|
Middle |
7.12 |
|
|
|||||
|
|
|
Bottom |
6.99 |
6.99 / 6.96 |
|
|
||||
|
|
07-Nov-11 |
Surface |
27.75 |
7.19 |
6.84 / 6.81 |
8.07 |
3.54 |
|
5.28 |
|
|
|
|
Middle |
7.27 |
|
|
|||||
|
|
|
Bottom |
7.34 |
6.99 / 6.96 |
|
|
||||
|
|
09-Nov-11 |
Surface |
22.75 |
7.37 |
6.84 / 6.81 |
8.06 |
4.95 |
|
6.53 |
|
|
|
|
Middle |
7.48 |
|
|
|||||
|
|
|
Bottom |
7.37 |
6.99 / 6.96 |
|
|
||||
|
|
11-Nov-11 |
Surface |
24.85 |
7.15 |
6.84 / 6.81 |
8.11 |
3.58 |
|
5.73 |
|
|
|
|
Middle |
7.21 |
|
|
|||||
|
|
|
Bottom |
7.26 |
6.99 / 6.96 |
|
|
||||
|
|
14-Nov-11 |
Surface |
25.30 |
7.30 |
6.84 / 6.81 |
8.02 |
3.88 |
|
5.00 |
|
|
|
|
Middle |
7.20 |
|
|
|||||
|
|
|
Bottom |
7.31 |
6.99 / 6.96 |
|
|
||||
|
|
16-Nov-11 |
Surface |
27.62 |
6.98 |
6.84 / 6.81 |
8.04 |
5.28 |
|
9.12 |
|
|
|
|
Middle |
7.09 |
|
|
|||||
|
|
|
Bottom |
7.21 |
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) |
18-Nov-11 |
Surface |
27.85 |
6.98 |
6.84 / 6.81 |
8.05 |
2.95 |
10.35 / 13.15 |
4.88 |
14.10 / 18.08 |
|
|
|
Middle |
7.10 |
|
|
|||||
|
|
|
Bottom |
7.17 |
6.99 / 6.96 |
|
|
||||
|
|
21-Nov-11 |
Surface |
26.52 |
7.32 |
6.84 / 6.81 |
7.73 |
3.60 |
|
5.95 |
|
|
|
|
Middle |
7.26 |
|
|
|||||
|
|
|
Bottom |
7.29 |
6.99 / 6.96 |
|
|
||||
|
|
23-Nov-11 |
Surface |
24.43 |
7.96 |
6.84 / 6.81 |
7.78 |
4.73 |
|
5.97 |
|
|
|
|
Middle |
8.05 |
|
|
|||||
|
|
|
Bottom |
8.08 |
6.99 / 6.96 |
|
|
||||
|
|
25-Nov-11 |
Surface |
26.37 |
7.17 |
6.84 / 6.81 |
7.79 |
7.71 |
|
9.97 |
|
|
|
|
Middle |
7.12 |
|
|
|||||
|
|
|
Bottom |
7.22 |
6.99 / 6.96 |
|
|
||||
|
|
28-Nov-11 |
Surface |
23.17 |
7.35 |
6.84 / 6.81 |
7.92 |
5.83 |
|
8.33 |
|
|
|
|
Middle |
7.28 |
|
|
|||||
|
|
|
Bottom |
7.35 |
6.99 / 6.96 |
|
|
||||
|
|
30-Nov-11 |
Surface |
23.27 |
7.21 |
6.84 / 6.81 |
7.88 |
5.89 |
|
5.75 |
|
|
|
|
Middle |
7.29 |
|
|
|||||
|
|
|
Bottom |
7.26 |
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) |
02-Nov-11 |
Surface |
27.58 |
7.20 |
- / - |
8.07 |
6.35 |
- / - |
7.47 |
- / - |
|
|
|
Middle |
7.15 |
|
|
|||||
|
|
|
Bottom |
7.28 |
- / - |
|
|
||||
|
|
04-Nov-11 |
Surface |
27.77 |
7.03 |
- / - |
8.10 |
3.55 |
|
5.12 |
|
|
|
|
Middle |
6.94 |
|
|
|||||
|
|
|
Bottom |
7.04 |
- / - |
|
|
||||
|
|
07-Nov-11 |
Surface |
27.80 |
7.31 |
- / - |
8.07 |
3.58 |
|
3.87 |
|
|
|
|
Middle |
7.19 |
|
|
|||||
|
|
|
Bottom |
7.29 |
- / - |
|
|
||||
|
|
09-Nov-11 |
Surface |
22.70 |
7.30 |
- / - |
8.05 |
5.13 |
|
6.37 |
|
|
|
|
Middle |
7.42 |
|
|
|||||
|
|
|
Bottom |
7.52 |
- / - |
|
|
||||
|
|
11-Nov-11 |
Surface |
24.85 |
7.23 |
- / - |
8.10 |
3.78 |
|
5.30 |
|
|
|
|
Middle |
7.21 |
|
|
|||||
|
|
|
Bottom |
7.41 |
- / - |
|
|
||||
|
|
14-Nov-11 |
Surface |
25.32 |
7.18 |
- / - |
8.02 |
3.96 |
|
6.53 |
|
|
|
|
Middle |
7.27 |
|
|
|||||
|
|
|
Bottom |
7.39 |
- / - |
|
|
||||
|
|
16-Nov-11 |
Surface |
27.62 |
7.20 |
- / - |
8.03 |
5.30 |
|
9.10 |
|
|
|
|
Middle |
7.27 |
|
|
|||||
|
|
|
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) |
18-Nov-11 |
Surface |
27.87 |
7.13 |
- / - |
8.05 |
3.02 |
- / - |
5.53 |
- / - |
|
|
|
Middle |
7.21 |
|
|
|||||
|
|
|
Bottom |
7.09 |
- / - |
|
|
||||
|
|
21-Nov-11 |
Surface |
26.53 |
7.08 |
- / - |
7.73 |
3.68 |
|
6.17 |
|
|
|
|
Middle |
7.17 |
|
|
|||||
|
|
|
Bottom |
7.09 |
- / - |
|
|
||||
|
|
23-Nov-11 |
Surface |
24.40 |
8.03 |
- / - |
7.78 |
4.80 |
|
4.78 |
|
|
|
|
Middle |
7.92 |
|
|
|||||
|
|
|
Bottom |
7.86 |
- / - |
|
|
||||
|
|
25-Nov-11 |
Surface |
26.42 |
7.20 |
- / - |
7.78 |
7.80 |
|
10.72 |
|
|
|
|
Middle |
7.15 |
|
|
|||||
|
|
|
Bottom |
7.14 |
- / - |
|
|
||||
|
|
28-Nov-11 |
Surface |
23.17 |
7.38 |
- / - |
7.93 |
6.56 |
|
6.42 |
|
|
|
|
Middle |
7.30 |
|
|
|||||
|
|
|
Bottom |
7.22 |
- / - |
|
|
||||
|
|
30-Nov-11 |
Surface |
23.23 |
7.42 |
- / - |
7.86 |
6.31 |
|
5.98 |
|
|
|
|
Middle |
7.52 |
|
|
|||||
|
|
|
Bottom |
7.41 |
- / - |
|
|
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) |
02-Nov-11 |
Surface |
27.82 |
7.24 |
7.02 / 6.94 |
8.09 |
5.64 |
11.87/13.44 |
9.23 |
13.25/14.39 |
|
|
|
Middle |
7.17 |
|
|
|||||
|
|
|
Bottom |
7.37 |
6.7 / 6.48 |
|
|
||||
|
|
04-Nov-11 |
Surface |
27.78 |
6.95 |
7.02 / 6.94 |
8.11 |
3.03 |
|
5.45 |
|
|
|
|
Middle |
7.05 |
|
|
|||||
|
|
|
Bottom |
6.93 |
6.7 / 6.48 |
|
|
||||
|
|
07-Nov-11 |
Surface |
27.33 |
7.37 |
7.02 / 6.94 |
8.04 |
4.92 |
|
5.90 |
|
|
|
|
Middle |
7.43 |
|
|
|||||
|
|
|
Bottom |
7.30 |
6.7 / 6.48 |
|
|
||||
|
|
09-Nov-11 |
Surface |
23.10 |
7.44 |
7.02 / 6.94 |
8.03 |
4.49 |
|
6.53 |
|
|
|
|
Middle |
7.36 |
|
|
|||||
|
|
|
Bottom |
7.43 |
6.7 / 6.48 |
|
|
||||
|
|
11-Nov-11 |
Surface |
24.42 |
7.39 |
7.02 / 6.94 |
8.07 |
6.84 |
|
5.37 |
|
|
|
|
Middle |
7.31 |
|
|
|||||
|
|
|
Bottom |
7.46 |
6.7 / 6.48 |
|
|
||||
|
|
14-Nov-11 |
Surface |
25.60 |
7.16 |
7.02 / 6.94 |
8.02 |
4.00 |
|
6.73 |
|
|
|
|
Middle |
7.24 |
|
|
|||||
|
|
|
Bottom |
7.30 |
6.7 / 6.48 |
|
|
||||
|
|
16-Nov-11 |
Surface |
27.68 |
7.21 |
7.02 / 6.94 |
8.06 |
5.16 |
|
7.55 |
|
|
|
|
Middle |
7.29 |
|
|
|||||
|
|
|
Bottom |
7.21 |
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) |
18-Nov-11 |
Surface |
24.63 |
7.31 |
7.02 / 6.94 |
8.23 |
5.55 |
11.87/13.44 |
9.10 |
13.25/14.39 |
|
|
|
Middle |
7.31 |
|
|
|||||
|
|
|
Bottom |
7.36 |
6.7 / 6.48 |
|
|
||||
|
|
21-Nov-11 |
Surface |
26.75 |
7.06 |
7.02 / 6.94 |
7.83 |
3.89 |
|
9.87 |
|
|
|
|
Middle |
7.15 |
|
|
|||||
|
|
|
Bottom |
7.30 |
6.7 / 6.48 |
|
|
||||
|
|
23-Nov-11 |
Surface |
24.20 |
7.69 |
7.02 / 6.94 |
7.77 |
6.81 |
|
8.42 |
|
|
|
|
Middle |
7.57 |
|
|
|||||
|
|
|
Bottom |
7.57 |
6.7 / 6.48 |
|
|
||||
|
|
25-Nov-11 |
Surface |
26.58 |
7.14 |
7.02 / 6.94 |
7.80 |
5.68 |
|
7.50 |
|
|
|
|
Middle |
7.22 |
|
|
|||||
|
|
|
Bottom |
7.29 |
6.7 / 6.48 |
|
|
||||
|
|
28-Nov-11 |
Surface |
23.55 |
7.21 |
7.02 / 6.94 |
7.91 |
8.85 |
|
10.18 |
|
|
|
|
Middle |
7.27 |
|
|
|||||
|
|
|
Bottom |
7.30 |
6.7 / 6.48 |
|
|
||||
|
|
30-Nov-11 |
Surface |
23.23 |
7.43 |
7.02 / 6.94 |
8.10 |
5.90 |
|
5.32 |
|
|
|
|
Middle |
7.51 |
|
|
|||||
|
|
|
Bottom |
7.43 |
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) |
02-Nov-11 |
Surface |
27.85 |
7.29 |
- / - |
8.10 |
5.98 |
|
7.50 |
- / - |
|
|
|
Middle |
7.43 |
|
|
|||||
|
|
|
Bottom |
7.49 |
- / - |
|
|
||||
|
|
04-Nov-11 |
Surface |
28.05 |
6.91 |
- / - |
8.12 |
3.09 |
|
4.65 |
|
|
|
|
Middle |
6.99 |
|
|
|||||
|
|
|
Bottom |
7.05 |
- / - |
|
|
||||
|
|
07-Nov-11 |
Surface |
27.33 |
7.29 |
- / - |
8.03 |
4.86 |
|
6.08 |
|
|
|
|
Middle |
7.36 |
|
|
|||||
|
|
|
Bottom |
7.43 |
- / - |
|
|
||||
|
|
09-Nov-11 |
Surface |
23.13 |
7.29 |
- / - |
8.03 |
4.62 |
|
7.48 |
|
|
|
|
Middle |
7.37 |
|
|
|||||
|
|
|
Bottom |
7.34 |
- / - |
|
|
||||
|
|
11-Nov-11 |
Surface |
24.50 |
7.28 |
- / - |
8.07 |
6.90 |
|
5.07 |
|
|
|
|
Middle |
7.37 |
|
|
|||||
|
|
|
Bottom |
7.42 |
- / - |
|
|
||||
|
|
14-Nov-11 |
Surface |
25.55 |
7.23 |
- / - |
8.01 |
4.21 |
|
7.58 |
|
|
|
|
Middle |
7.30 |
|
|
|||||
|
|
|
Bottom |
7.20 |
- / - |
|
|
||||
|
|
16-Nov-11 |
Surface |
27.82 |
7.12 |
- / - |
8.07 |
5.22 |
|
7.92 |
|
|
|
|
Middle |
7.22 |
|
|
|||||
|
|
|
Bottom |
7.30 |
- / - |
|
|
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) |
18-Nov-11 |
Surface |
24.63 |
7.29 |
- / - |
8.23 |
5.70 |
- / - |
10.12 |
- / - |
|
|
|
Middle |
7.27 |
|
|
|||||
|
|
|
Bottom |
7.31 |
- / - |
|
|
||||
|
|
21-Nov-11 |
Surface |
26.77 |
7.28 |
- / - |
7.83 |
4.02 |
|
9.78 |
|
|
|
|
Middle |
7.12 |
|
|
|||||
|
|
|
Bottom |
7.07 |
- / - |
|
|
||||
|
|
23-Nov-11 |
Surface |
24.15 |
7.59 |
- / - |
7.77 |
6.84 |
|
8.70 |
|
|
|
|
Middle |
7.71 |
|
|
|||||
|
|
|
Bottom |
7.66 |
- / - |
|
|
||||
|
|
25-Nov-11 |
Surface |
26.63 |
7.21 |
- / - |
7.80 |
5.75 |
|
7.03 |
|
|
|
|
Middle |
7.29 |
|
|
|||||
|
|
|
Bottom |
7.35 |
- / - |
|
|
||||
|
|
28-Nov-11 |
Surface |
23.60 |
7.28 |
- / - |
7.91 |
8.94 |
|
10.48 |
|
|
|
|
Middle |
7.31 |
|
|
|||||
|
|
|
Bottom |
7.25 |
- / - |
|
|
||||
|
|
30-Nov-11 |
Surface |
23.27 |
7.33 |
- / - |
8.10 |
5.69 |
|
6.37 |
|
|
|
|
Middle |
7.46 |
|
|
|||||
|
|
|
Bottom |
7.51 |
- / - |
|
|
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 Summary of Project-Related Exceedances
4.4.1
Table 4-9 summarises
the project-related exceedance results recorded in November 2011. 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 |
|
Air Borne
Noise |
25 |
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) |
3,214.1 |
|
Inert C&D
Material Reused in this Contract (m3) |
325.0 |
|
Inert C&D Material
Reused in other Contracts* (m3) |
13,640.0 |
|
Metals Generated (kg) |
10.0 |
|
Paper / Cardboard
Packaging (kg) |
400.0 |
|
Plastics (kg) |
10.0 |
|
Chemical Waste (kg) |
Nil |
|
General Waste Disposed of to NENT
Landfill (m3) |
34.5 |
* Other Contracts include CV/2009/14,
DC/2007/08, HY/2007/09, HY/2007/10, HY/2008/09, YL/2009/01, XRL823A & 823B,
TW7, Tailor Recycle Aggregate and Wo Shang Wai.
Table
5-1 Waste Generated in November 2011
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 |
|
3 November 2011 |
1.
The wastewater treatment
facility for Portion E shall be improved. |
1.
The Contractor was
reminded to improve the design of the wastewater treatment facility. |
1. A treatment device with filter was set up to treat the wastewater
prior to discharge on 7 November 2011. (Closed) |
|
18 November
2011 |
1.
Location for temporary allocated
air compressor should be reviewed at Intake I-2. |
1.
The Contractor was
reminded to review the location for temporary allocated air compressor. |
1. The air compressor under the bridge at Intake I-2 was removed on 24
November 2011. (Closed) |
Table 6-1 Site Inspection by ET
7.1.1
A complaint hotline
at 9850 3241 of the Contractor has been established for the
Project.
7.1.2
No environmental complaint
was received during the reporting month. Details of the complaint
investigation and observations can be referred to Appendix K.
7.1.3
Cumulative statistics of
environmental complaints are shown in Table 7-1.
|
Complaints Received in the
Reporting Month |
Cumulative Number of Complaints |
|
0 |
23 |
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 |
||
|
November 2011 |
Cumulative |
November 2011 |
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
Outfall, I-1, I-2 and I-3;
·
TBM drilling of the tunnel and
mucking out of tunnel spoil at Outfall;
·
Construction of spiral ramp
structure at Outfall;
·
Construction of box culvert and
L-shaped retaining wall at Outfall;
·
Placing leveling stone for
formation of sea wall at Portion E;
·
Installation of precast panels
for construction of outfall apron at Portion E;
·
Drilling and excavation of vortex
shaft at I-3;
·
Reinstatement of slope at PB wall
at I-3;
·
Construction of approach channel
at I-3;
·
Blasting and excavation for man
access shaft and vortex drop shaft at I-2;
·
Construction of approach channel
structure at I-2;
·
Construction of drainage works at
Portion G at I-2; and
·
Preparation for TBM retrieval 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 |