Improvements to
San Tin Interchange (Contract No. HY/2004/09)
Monthly
Environmental Monitoring & Audit Report
Report
No. 1517
August October 2006
Client : Chun Wo Construction &
Engineering Co., Ltd. |
Contract
No.: |
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Project Title : Improvements to San Tin Interchange (Contract No. HY/2004/09) |
Project No.:
3878 |
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Document No.: 3878-OR025 |
Controlled Copy No.: |
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Document
Title: Monthly Environmental Monitoring
& Audit Report No. 17 |
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Covering
Letter / Transmittal Ref. No.: 3878/ 63 |
Date of Issue:
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Revision,
Review and Approval Records |
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00 |
Monthly EM&A Report No. 17 |
Various/ 14 |
Henry Ng/ 14 |
Susana Bezy/ 14 |
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Revision |
Description |
Prepared by / date |
Reviewed by / date |
Approved by / date |
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Distribution
(if insufficient space, please use separate paper)
Controlled Copy No. |
Issued to |
01 – 04 |
EPD |
05 – 06 |
Maunsell |
07 |
Chun Wo |
08 |
ERM |
09 |
ACL |
1.1 Works undertaken during the Reporting Period
1.2 Environmental Permit and Licences
1.3 Environmental
Document Submissions to EPD
1.4 Environmental
Monitoring Locations
2 Environmental Measures and Implementation Status
3.3 Landscape and
Visual Resources
3.4 Ad-hoc Air Quality Monitoring
4.3 Environmental
Non-compliance
4.4 Environmental Complaint and Prosecution
5.1 Key Issues for the Coming Months
5.2 Monitoring Schedules for the Next Month
List of Annexes
Annex A Contractor’s Works Programme
Annex B Mitigation Measures Checklist
Annex C Calibration Certificates
Annex D Noise Monitoring Results
Annex E Water Quality Visual Inspection Reports
Annex F Landscape & Visual Resources Inspection Reports
Annex G Weekly Site Inspection Reports
Annex H Notification
of Environmental Exceedances and Non-compliance Forms and Non-Compliance Forms
Annex I Action and Limit Levels
Annex J Cumulative Statistics on Complaints, Notifications of Summons and Successful Prosecutions
List of Tables
Table 1.1 Details of Permits and Licenses issued in October 2006
Table 1.2 Summary of Environmental Submissions to EPD in October
2006
Table 1.3 Noise
Monitoring Stations
Table 3.1 Summary
of Noise Monitoring Results during Normal Working Hours
Table 3.4 Summary of Waste Disposal for October 2006
Table 5.1 Proposed
Noise Monitoring Schedule for November 2006
List of Figures
Figure 1 Site Plan & Locations of Noise and Air Quality Monitoring Stations
Executive Summary
Atkins China
Limited (ACL) has been appointed by Chun Wo Construction & Engineering Co.,
Ltd. to implement the Environmental Monitoring and Audit (EM&A) programme
for the construction works under Contract No. HY/2004/09 Improvements to San
Tin Interchange (hereinafter, the Project).
The
construction of the Project commenced since 21st June 2005. This report is the fourteenth fifseventhteenth monthly EM&A report for the
Project which summarises the monitoring results and audit findings during the
reporting period from 1st October 2006 to 331st 1st AugustOctober 2006.
Environmental
Monitoring and Audit Progress
The monthly
EM&A programme was undertaken in accordance with the EM&A Manual. A summary of the monitoring activities
in this reporting period is listed below:
·
Weekly site inspections were undertaken jointly with
the Contractor and Engineer’s Representative (ER) on 3rd5th3rd,
120th,
17th 5th,24th and
31th3126th Octost berAugust
2006. The Independent Environmental
Checker (IEC) joined the site inspection on 264th August October 2006.
·
Noise monitoring at three designated monitoring
stations was undertaken on 3rd1st,
111th,
17th, 2319th,
27th rdand 30th 31st August October 2006 during
normal working hours; and on 1st, 8th, 15th,
22nd, 243th, 25th and 29th 31st AugustOctober 2006 during the
restricted hour periods on a weekly basis when there were construction activities
scheduled during those periods. Also, o One ad-hoc
monitoring was undertaken on 12th August
2006 in response to following an exceedance of lLimit lLevel recorded on 11th August
2006.
·
Visual site surveillance for water quality was
undertaken three times a week.
·
Site inspections for landscape and visual resources
were undertaken on 188th and 30258th August October 2006.
Breaches of
Action and Limit Levels
There were totally seven seven records of environmental
exceedances during the reporting period, of which six were recorded during the
reporting period, of which six were recorded during restricted
hours noise monitoring on 1st6th,
83th,
15th, 22nd, 24th, 25th 20th, 27th and
3129th st August October 2006, and one was
recorded on 18th October 2006 with
respect to excavation at the identified contaminated area at site A prior to
approval of the submitted Contamination Assessment Report (CAR) and
Remediation Action Plan (RAP) for Sites A and E by
EPD.
, and one was recorded during normal working hours
noise monitoring on 11th August
2006.
For the restricted hours noise monitoring,For
the restricted hours noise monitoring, the exceedances were proved not to have been caused by the site activities of the Contractor.
Environmental Non-Compliance
There was one environmental non-compliance recorded on
18th October 2006 during this reporting period which was due
to excavation at the contaminated area at site A prior to EPD’s approval of the
submitted CAR / RAP (Sites A and E). Relevant
parities were immediately notified and the excavation was stopped. The stockpile of excavated
material was stockpiled on-site and covered by tarpaulin sheet on the top and
at the bottom. The Contractor has implemented mitigation measures which were
identified by the ET.
There was one The environmental
exceedance recorded during and one
non-compliance regarding to the normal working hours noise monitoring was due to
the measured Leq (30min) at on Monitoring Station CM1
was found to exceeding the Limit Level of
75dB(A), which was not in compliance with the requirements mentioned in EIA
Report and EM&A Manual. During the measurement period, concrete breaking
using a breaker was being undertaken at the Slip Road
A works area at side of San Tin Highway. The Contractor was advised to stop the
concrete breaking works in the concerned area immediately to avoid further
exceedances. Following the Event and Action Plan for
construction noise, additional noise measurement was conducted on the following
day (12th August 2006) during which no concrete breaking activity
was being undertaken. The measured Leq (30min) noise level was found to be
67dB(A). Thus, the Contractor was advised to provide mitigation measures as necessary such as and reminded
that movable noise barriers should be provided to avoid exceedances caused
by prior to any further site concrete breaking works in
the concerned area following the recommendations in Section 3.47 and Figure 3.5
of the Project EIA Report. Further to discussion with the Contractor, no
further concrete breaking activities will be required in the concerned area.
Following the Event and Action Plan for construction noise, additional noise
measurement was conducted on the following day (12th August
2006) in which no concrete breaking activity was being undertaken. The measured
Leq (30min) noise level was found to be 67dB(A).
Complaint Log
No
environmental complaints were received during this reporting period.
Notifications
of Summons and Prosecutions
There were no
notifications of summons or prosecutions received during this reporting period.
Reporting
Changes
This report
has been developed in compliance with the reporting requirements for the
subsequent monthly EM&A reports as required by the Project EM&A Manual.
Future Key
Issues
The key issues with respect to
the works in the forthcoming 2 months include:
·
Laying
of drainage pipes;
·
Road
widening works;
·
Trench
works;
·
Storage
and preparation of precast viaduct segments;
· Erection of precast viaduct segments;
· Installation of parapet walls; and
·
Installation of noise barrier.
Installation
of viaduct segments will continue in September October 2006.
The Contamination Assessment
Report (CAR) and Remediation Action Plan (RAP) of Site A and Site E will be
finalized and submitted after fFurther
sampling at Site A in response to ER’s comments on the Contamination Assessment
Report (CAR) and Remediation Action Plan (RAP) of Site A and Site E was conducted in August 2006. The CAR / RAP (Sites A and E) CAR and RAwere submitted to EPDfinalized in October 2006 and are currently being under reviewedwill be finalized upon
receipt of the analysis results.
1.1
Works undertaken during the Reporting
Period
The major
construction activities undertaken during this reporting period are summarised
below:
·
Bored piling;
· Laying of drainage pipes;
· Road widening works;
· Trench works;
· Storage and preparation of precast viaduct segments; and
· Erection of precast viaduct segments.
The site plan
of the Project is shown in Figure 1.
The Contractor’s works programme is provided in Annex A.
1.2
Environmental Permit and Licences
There were no changes or clarification to the Environmental Permit (EP-190/2004) during the reporting period.
Seven One Construction Noise Permit (CNP) was issued
in August
October 2006. Details of the CNP are summarised in Table 1.1. One
CNP (Permit No. PP-RN0026-06)
for carrying out percussive piling works from 15th August 2006 to 13th November 2006 was issued on 31st July 2006 and
received by the Contractor in August 2006.
Table 1.1 Details of Permits and Licenses issued in August October 2006
Permit /
License |
Reference No. |
Issue Date |
Expiry
Date |
Construction Noise Permit for
general construction work |
GW-RN0500-06 |
6th
October 2006 |
30th
December 2006 |
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1.3
Environmental
Document Submissions to EPD
A summary
of the status of the submissions to EPD as provided during the month of August October 2006 is presented
in Table 1.2.
Table 1.2 Summary
of Environmental Submissions to EPD in August October 2006
Item No. |
Document
Title |
Date of Submission |
1 |
Monthly EM&A Report No.
16 for September 2006 |
12th October 2006 |
|
Contamination
Assessment Report (CAR) and Remediation Action Plan (RAP) for Sites A And E |
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1.4
Environmental Monitoring Locations
Noise monitoring was undertaken at three monitoring stations CM1, CM2 and CM3. The locations are shown on Figure 1. Description of these monitoring stations is provided in Table 1.3.
Table 1.3 Noise Monitoring Stations
Monitoring
Station ID |
Description |
Easting |
Northing |
CM1 |
Village house near San Tin Highway |
826133 |
839839 |
CM2 |
Village house near San Tin Highway |
826291 |
839918 |
CM3 |
Village house near Kwu Tung Road |
826605 |
840076 |
The
mitigation measures listed in the Project EIA Report, EM&A Manual and
Environmental Permit and the implementation status are provided in Annex B.
Based on site inspection findings, the Contractor has implemented
the required mitigation measures during construction works to date in general. It was identified on 18th
October 2006 that the identified contaminated area at Site A was excavated by
the Contractor. Relevant parties
were immediately informed and excavation at the concerned area was stopped. A
notification of non-compliance form was subsequently issued. Details about the notification are
described in the following sections.
3.1.1 Noise Monitoring Equipment
Details of
the noise monitoring equipment are listed below and the calibration
certificates are presented in Annex C:
· Sound level meter ONO-SOKKI LA-5110
· Acoustical calibrator ONO-SOKKI SC-2110
· Hand-held anemometer
3.1.2 Noise Monitoring Methodology
The sound
level meter was calibrated with an acoustical calibrator prior to each
measurement. It was set on a
tripod at 1.2 m above local ground level at the monitoring station. Measurement of the A-weighted Leq(30
minutes) noise level for normal daytime hours was undertaken. Three consecutive A-weighted Leq(5
minutes) noise levels were measured for restricted hours monitoring. Wind speed was checked during the
monitoring period using the hand-held anemometer to ensure steady wind speed
did not exceed 5 m/s, or gusts did not exceed 10 m/s. After the noise measurement the sound level meter was
re-calibrated using the acoustical calibrator.
3.1.3 Noise Monitoring Results
Noise
monitoring was undertaken on a weekly basis when noise generating activities
were underway. The noise
monitoring results obtained in August October 2006, during the normal working hours;
restricted hours from 1900 to 2300 hours on normal working days and from 0700
to 1900 hours on general holidays;, and restricted hours from 2300 to
0700 hours of next day and restricted hours from 2300 to 0700 hours of
next day are summarised in Table 3.1,, Table 3.2
Table 3.2 and
Table 3.33, respectively. There was were no environmental
exceedances of the Actione and Limit Levels for environmental exceedance of
the Action and Limit Levels for noise monitoring recorded during
the normal daytime hours within the reporting period and but six six notification of exceedances were reported during
the rrestricted
hours.
Details of the monitoring time period and weather condition during the monitoring period and the graphical presentation of the noise monitoring results are provided in Annex D.
Table 3.1 Summary of
Noise Monitoring Results during Normal Working Hours
Date
of Monitoring |
Normal Hours. Noise Monitoring
Results Leq(30 minutes) dB(A) |
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CM1 |
CM2 |
CM3 |
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3rd October 2006 |
65 |
75 |
66 |
11th October 2006 |
67 |
71 |
67 |
19th October 2006 |
66 |
71 |
64 |
27th October 2006 |
66 |
71 |
63 |
31st October 2006 |
67 |
72 |
64 |
Remarks:
(1) CM2 is a non-façade measurement location. A positive correction of
3dB(A) has been applied to the measured noise level at CM2 according to EPD’s
guideline.
Table 3.2 Summary
of Noise Monitoring Results during Restricted Hours – All days during the evening (1900 to 2300 hours), and general holidays
(including Sundays) during the day-time and evening (0700-2300 hours)
Date of Monitoring |
Restricted
Hours Noise Monitoring Results Leq(15 minutes) dB(A) |
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CM1 |
CM2 |
CM3 |
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1st
October 2006 |
64 |
75 |
63 |
8th
October 2006 |
63 |
69 |
61 |
15th
October 2006 |
63 |
68 |
60 |
22nd
October 2006 |
65 |
71 |
58 |
24th
October 2006 |
63 |
69 |
57 |
29th
October 2006 |
63 |
69 |
60 |
(1)
CM2 is a non-façade measurement location. A positive correction of
3dB(A) has been applied to the measured noise level at CM2 according to EPD’s
guideline.
(2)
Underlined figure indicates exceedance of the Limit Level of 65dB(A).
Table 3.3 Summary of Noise Monitoring Results
during Restricted Hours – All days during the night-time (2300 to 0700 hours)
Date
of Monitoring |
Restricted Hours Noise Monitoring
Results Leq(15 minutes) dB(A) |
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CM1 |
CM2 |
CM3 |
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24th October 2006 |
65 |
69 |
55 |
Remark:
(1) CM2 is a non-façade measurement location. A positive
correction of 3dB(A) has been applied to the measured noise level at CM2
according to EPD’s guideline.
(2) Underlined figure indicates exceedance of the Limit Level of
50dB(A).
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Remark:
(1)
CM2 is a non-façade measurement location. A
positive correction of 3dB(A) has been applied to the measured noise level at
CM2 according to EPD’s guideline.
(1)
Underlined figure indicates exceedance of the Limit
Level of 50dB(A).
(1)
Time of measurement at CM3 started after 23:59
hours (midnight) of Tthe “Date of
Monitoring” stated in the table. Therefore, the “Date of Monitoring” for CM3 refers to 18th and 1st September 2006,
respectively refers to the date of which nighttime noise
monitoring started.
Visual site
surveillances for water quality were undertaken three times a week. Based on the visual inspection results,
the Contractor has followed all necessary site practices for the maintenance of
the site drainage system, such as Regular
and prompt rremoval of stagnant water pools
to prevent mosquito breeding.
The details of the water quality visual inspection
reports are provided in Annex E.
3.3
Landscape and
Visual Resources
Two site
inspections on the landscape and visual resources were undertaken in August October 2006.
During
the first inspection, some trees (about 10 trees) inside transplantation nursery
in N1 Division area were found to have been cut down. The Contractor advised that those trees were found dead and
were removed under instruction of the Engineer’s Landscape Architect. Some trees inside transplantation
nursery in N2 Division area were found to have been removed by the Contractor.
The Contractor reported that those trees were found dead and removed under the
instruction of the Engineer’s Landscape Architect. Some new trees with smaller tree trunk diameter (less than
95 mm) were transplanted and labelled.
During
the second inspection, insufficient sandbags barriers were identified in
the transplantation nursery in the N2 Division area to prevent soils from
washing down. The Contractor was reminded to provide sufficient sandbags.The
Contractor was reminded to clear up the weeds regularly as proper
maintenance for the nursery.
Sandbags barrier encircling
the transplantation nursery in the N1 Division area was seen to have been
damaged. Some construction materials were seen to have accumulated on top of
the soil surface inside the nursery. The Contractor was reminded to clear up
the construction materials and place them in an appropriate storage area.
Damaged sandbags should be replaced by new ones to contain the soil
inside the nursery and prevent soil erosion.
Several trees inside the transplantation nursery in
the N2 Division aArea were
found to have fallen down during
the inspection on 15th
September 2006 due to the typhoon event in
early August 2006 and mid-September 2006. The Contractor
was reminded to replant these trees in the nursery to ensure their survival. The fallen trees were observed to have been replanted during inspection on 27th
September 2006.
The details of the
landscape and visual resources inspection reports are provided in Annex F.
3.4
Ad-hoc Air Quality Monitoring
No ad-hoc air quality monitoring
was required during the reporting period.
The Contractor has adopted a trip ticket
system for the disposal of construction wastes. According to the records provided by the Contractor, the
disposal of construction waste within the reporting period is summarised in Table 3.3Table 3.4Table 3.4Table 3.4.
Table 3.3444 Summary of Waste Disposal for August October 2006
Waste Type |
Destination |
No. of Trips |
Quantity |
C&D Waste |
NENT Landfill |
21 |
105 m3 |
C&D Waste |
WENT Landfill |
3 |
15 m3 |
Building debris |
CEDD’s Tuen Mun Area 38 Fill Bank |
41 |
205 m3 |
|
CEDD’s Tuen Mun Area 38 C&D Materials
Recycling Facility |
3 |
15 m3 |
Chemical Waste |
Collected by Dunwell Enviro-Tech (Holdings)
Ltd. |
1 |
900 L |
Chemical Toilet Waste |
Collected by Proenvironmental Services Ltd. |
24 |
- |
Sewage Holding Tank Waste |
Collected by Waylung Waste Services Ltd. |
14 |
- |
Site inspections were undertaken on 5th3rd,
120th,
17th 5th,24th and
31th3126th Octost berAugust
2006, and jointly with the IEC
on 264th August October 2006. Specific locations within the
site were identified during the inspection for improvements in proper
implementation of the environmental mitigation measures. These include:
· Prompt removal of stagnant water pools to prevent mosquito breeding.
· Regular collection of C&D waste and general refuse to keep good site tidiness.
· Handling of spent lubricant storage on site.
· Replacement of damaged tarpaulin covering the slope surface.
· Complete coverage of stockpile of excavated soil by tarpaulin to prevent dust emission.
The
record of the weekly site inspection findings is provided in Annex G.
4.2
Environmental Exceedances
During the reporting period, there were seven seven records of exceedances
of environmental criteria. Six of them were noise exceedances of Limit Level. Six of
which were noise exceedances of the lLimit lLevel
during restricted hours noise monitoring at CM1, CM2 and CM3, respectively, and
one was related to excavation at the contaminated area at site A prior to EPD’s
approval of the submitted CAR / RAP (Sites A and E).
For the noise exceedances, fFor the
exceedances of the lLimit lLevel
during restricted hours noise monitoring, the project-related works being undertaken
during the measurement period were located at a distance away (at least over
100m) from the monitoring stations.
The exceedances were due to the high ambient background noise caused by
road traffic on San Tin Highway.
Thus, the noise exceedances recorded were found not to be attributable
to project works.
For the exceedances of the lLimit lLevel
during normal working hours noise monitoring at CM1 on 11th August
2006, During
the measurement period, concrete breaking using a breaker was being undertaken at
the Slip Road
A works area at side of San Tin Highway which is about 30m away from CM1. The
Contractor was advised to stop the concrete breaking works in the concerned
area immediately. Following
the Event and Action Plan for construction noise, additional noise measurement
was conducted on the following day (12th August 2006) in which no
concrete breaking activity was being undertaken. The measured Leq (30min) noise
level was found to be 67dB(A).
Thus, the exceedance may have
been caused by the concrete breaking activities. urther investigation and discussion with ER identified that project-related works being undertaken during the
measurement period were located at a distance away (at least 1000m) from the
monitoring stations. The exceedances were due to the high ambient background
noise caused by road traffic on San Tin Highway. Thus, the noise exceedances recorded on
1st6th, 83th,
15th, 22nd, 24th, 25th 20th, 27th and
3129th st August October 2006 were found not to be attributable to the project worksthe Contractor, no further
concrete breaking activities will be required in the Slip Road A works
area. Nonetheless, the Contractor
was advised to implement necessary noise mitigation measures such as and reminded that movable
noise barriers (as recommended in the Project EIA Report) of 3 to
5m high with skid footing should be provided to avoid further
exceedances that would be caused by potential noisy prior
to any further site works in the concerned area
following the recommendations in Section 3.47 and Figure 3.5 of the Project EIA
Report. Further to discussion with the Contractor, no further concrete breaking
activities will be required in the concerned area.
On 18th October 2006 the contaminated area (TPH
contamination) at site A was found to have been excavated by the Contractor
while the submitted CAR / RAP (Sites A and E) has not yet been approved by EPD.
Relevant parities were immediately notified and
the excavation was stopped. The
stockpile of excavated material was stockpiled on-site and covered by tarpaulin
sheet on the top and at the bottom.
The excavation at the concerned area was not in compliance with the
requirements mentioned in Section 8.3 of the
EM&A Manual. Thus, a
notification of exceedance form was issued to the Contractor. A meeting with the Contractor, ET, ER
and IEC was subsequently held on site.Following the Event and Action Plan for
construction noise, additional noise measurement was conducted on the following
day (12th August 2006) in which no
concrete breaking activity was being undertaken. The measured Leq (30min) noise
level was found to be 67dB(A).
The Contractor’s implementation of the
following mitigation measures, are required:
· Excavation and construction works shall not be carried out at the concerned area until an approval of the CAR / RAP is received from EPD.
· Verification sampling shall be carried out and tested for TPH level in accordance with the procedures described in the CAR / RAP (Site A and E) in order to ensure complete removal of contaminated materials. As the soil at the edge of excavation has already exposed to atmosphere, samples shall be taken at the inner layers as much as possible at the side-walls and at the bottom of the excavation;
· Material already excavated from this concerned area (about 2m3) shall be properly stored on site and handled as contaminated material. The excavated material is currently stored on an existing concrete-paved ground floor. Tarpaulin sheets shall be used to cover the stockpile at the top and at the bottom. The Contractor shall ensure the stockpile is fully contained on-site by tarpaulin sheet and a layer of sandbag barrier shall be installed surrounding the stockpile in order to avoid any material from flushing away during heavy rainfall and to minimize wind erosion. Adequate fencing shall be provided surrounding the stockpile, and warning signs indicating “contaminated materials” shall be provided contained, only small quantity of leachate (if any) would be expected which shall be collected and treated by sedimentation and oil interceptor before discharge. The Contractor shall make sure adequate equipment / treatment facilities are readily available on site;
· Impervious sheeting shall be used to cover the excavated area and the exposed soil surface in order to minimize material from flushing away by rain and wind erosion. In case of heavy rainfall and water is collected inside the excavated location, the collected water shall also be collected and treated before discharge; and
· Workers must wear protective clothes, masks and personal protective equipment when works in this area and when handling excavated material.
Verification sampling, as described above, was
subsequently carried out by the Contractor on 20th October 2006.
Samples collected were delivered to a HOKLAS laboratory for testing TPH
level. The test results will be
reviewed when they become available.
Subsequent inspections identified that the
Contractor has implemented the recommended mitigation measures. An inspection was also carried out by
EPD on 24th October 2006.
No further comments were received from EPD.
With regard to the
above, records of the notification of environmental exceedances and the
non-compliance forms are provided in Annex H. The Action and Limit
Levels for impact monitoring are provided in Annex I.
4.3
Environmental
Non-compliance
During the
reporting period, one environmental non-compliance was recorded on 18th
October 2006 regarding to excavation at the contaminated area at site A
prior to EPD’s approval of the submitted CAR / RAP (Sites A and E). Relevant
parities were immediately notified and the excavation was stopped. The stockpile of excavated
material was stockpiled on-site and covered by tarpaulin sheet on the top and
at the bottom. A meeting with the Contractor, ET, ER and IEC was
subsequently held on site. Following
the Event and Action Plan for construction noise, additional noise measurement
was conducted on the following day (12th August
2006) in which no concrete breaking activity was being undertaken. The measured
Leq (30min) noise level was found to be 67dB(A). The
Contractor was advised to implement the mitigation
measures. Verification sampling was subsequently carried out by the Contractor on
20th October 2006 for testing TPH level.
Subsequent inspections identified
that the Contractor has implemented the recommended mitigation measures. An inspection was also carried out by
EPD on 24th October 2006.
No further comments were received from EPD.
With
regard to the above, record of the notification of environmental non-compliance
and
the non-compliance forms is provided in Annex H.
4.4
Environmental Complaint and Prosecution
During
the reporting period, no environmental complaints, prosecutions or summons were
received. Cumulative statistics on complaints, notifications of summons
and successful prosecutions for the Project are provided in Annex J.
5.1
Key Issues for the Coming Months
The key
issues with respect to the works in the forthcoming 2 months include:
· Laying of drainage pipes;
· Road widening works;
· Trench works;
· Storage and preparation of precast viaduct segments;
· Erection of precast viaduct segments;
· Installation of parapet walls; and
· Installation of noise barrier.
The CAR and RAP of Site A and Site E were submitted to EPDfinalized and are currently being under reviewedwill be finalized upon
receipt of the analysis results.The
Contamination Assessment Report (CAR) and Remediation Action Plan (RAP) of Site
A and Site E will be finalized including upon receipt of the analysis results of the further sampling to be
conducted at Site A.
5.2
Monitoring Schedules for the Next
Month
The
proposed schedule for noise monitoring in September November 2006 is provided
in Table
5.1 below:
Table
5.1 Proposed
Noise
Monitoring Schedule for September November 2006
Date |
Noise
Monitoring Station |
6th
|
CM1, CM2 and CM3 |
14 |
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21st November 2006 (Tuesday) |
CM1, CM2 and CM3 |
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CM1, CM2 and CM3 |
There
were six
six records
of exceedances of the noise Limit Level during the reporting period. However,
none of these are attributable to project works.
One
environmental exceedance form and one non-compliance form were also issued due
to excavation at the contaminated area at Site A prior to EPD’s approval of the
submitted CAR/RAP (Sites A and E).
There was one exceedance
non-compliance
of the Limit Level recorded during the normal hours
noise monitoring due to concrete breaking activities in project works area
during the reporting period.
No environmental complaints, prosecutions or summons was received during the reporting period.