Improvements to
San Tin Interchange (Contract No. HY/2004/09)
Monthly
Environmental Monitoring & Audit Report
Report No. 1519
August December 2006
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
Annex I Action and Limit Levels
Annex J Cumulative Statistics on Complaints, Notifications of Summons and Successful Prosecutions
List
of Tables
Table 1.1 Summary of Environmental Submissions to EPD in December 2006
Table 1.2 Noise Monitoring Stations
Table 3.1 Summary of Noise Monitoring Results during Normal Working Hours
Table 3.3 Summary of Waste Disposal for December 2006
Table 5.1 Proposed Noise Monitoring Schedule for January 2007
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 fifninethteenth monthly EM&A report for the
Project which summarises the monitoring results and audit findings during the
reporting period from 1st December 2006 to 331st
1st AugustDecember 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 3rd7th3rd, 140th,
21st 5th,24th and
31th3128th Decemst berAugust
2006. The Independent Environmental
Checker (IEC) joined the site inspection on 21st August December 2006.
·
Noise monitoring
at three designated monitoring stations was undertaken on 6th1st,
121th,
17th, 2318th
rdand
30th 28th
August December 2006 during normal working hours; and on
3rd, 17th, 24th and 31st 31st AugustDecember
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 158th and 30308th
August December 2006.
Breaches
of Action and Limit Levels
There were totally seven four records of environmental
exceedances during the reporting period, of which six were recorded
during restricted hours noise monitoring on 3rd, 17th,
24th and 31st 31st AugustDecember
2006. However, , and one was recorded
during normal working hours noise monitoring on 11th August
2006.
For the
restricted hours noise monitoring,all the
exceedances were proved not to have been caused by the site activities of the
Contractor and were attributable to the high ambient traffic noise from San Tin
Highway.
Environmental
Non-Compliance
No environmental non-compliances were received during this reporting period.
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.
The Contamination Assessment Report (CAR) and Remediation Action Plan
(RAP) of Site A & Site E were approved by EPD on 8th December
2006. Additional verification sampling at Site A was conducted on 16th
December 2006 and would continue in January 2007.
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;
· Erection of precast viaduct segments and
· Installation of parapet walls..
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.
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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
December 2006
is presented in Table 1.1.
Table 1.1 Summary of Environmental Submissions to EPD in August December 2006
Item No. |
Document
Title |
Date of Submission |
1 |
Monthly EM&A Report
No. 18 for November 2006 |
13th December 2006 |
|
Quarterly EM&A Report No. 6 (September 2006
– November 2006) |
|
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 1.2.
Table 1.2 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.
The Contamination Assessment Report (CAR) and Remediation Action Plan
(RAP) of Site A & Site E were approved by EPD on 8th December
2006. Additional verification
sampling at Site A as recommended in the approved report was conducted on 16th
December 2006 and would continue in January 2007.
Based on the
site inspection findings, the
Contractor has implemented the required mitigation measures during construction works to date in general.
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, Rion NA-27
· Acoustical calibrator ONO-SOKKI SC-2110, Rion NC-73
· 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 December 2006, during the
normal working hours; restricted hours from 0700 to 1900 hours on general
holidays and restricted hours from 2300 to 0700 hours of
next day are summarised in Table 3.1 and, Table
3.2 Table 3.23, 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 four notifications 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) |
||
CM1 |
CM2 |
CM3 |
|
6th December 2006 |
67 |
72 |
68 |
12th December 2006 |
66 |
71 |
63 |
18th December 2006 |
67 |
72 |
65 |
28th December 2006 |
68 |
72 |
64 |
Remarks:
(1) CM2
is a non-façade measurement location. A positive correction of 3dB(A) has been
applied to the measured noise levels 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) |
||
CM1 |
CM2 |
CM3 |
|
3rd
December 2006 |
64 |
69 |
59 |
17th
December 2006 |
62 |
67 |
58 |
24th
December 2006 |
65 |
71 |
60 |
31st
December 2006 |
64 |
71 |
59 |
(1) CM2 is a non-façade measurement
location. A positive correction of 3dB(A) has been applied to the measured
noise levels at CM2 according to EPD’s guideline.
(2) Underlined figure indicates
exceedance of the Limit Level of 65dB(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,
including:
·
Regular and prompt Rremoval of
stagnant water pools to prevent mosquito breeding;
·
Proper diversion of surface runoff to site drainage
systemProvision of.
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 December 2006.
During the
first inspection, insufficient sandbags barrier was provided in the
transplantation nursery behind the site office in the N1 Division area. The
Contractor was reminded to provide sufficient sandbags to prevent soil from
being washed down and this was seen to have been implemented during the second inspection. The Contractor was advised to regularly
maintain the sandbags barrier at the transplantation nurseries. 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 3.3.
Table 3.3 Summary of Waste Disposal for December 2006
Waste
Type |
Destination |
No.
of Trips |
Quantity |
C&D Waste |
NENT Landfill |
19 |
95 m3 |
Building debris |
CEDD’s Tuen Mun Area 38 Fill Bank |
31 |
155 m3 |
Chemical Waste |
Collected by Dunwell Enviro-Tech (Holdings)
Ltd. |
2 |
1800 L |
Chemical Toilet Waste |
Collected by Proenvironmental Services Ltd. |
12 |
- |
Sewage Holding Tank Waste |
Collected by Waylung Waste Services Ltd. |
12 |
- |
Site inspections were undertaken
on 7th, 14th3rd,
21st 5th,24th and
31th3128th Decemst berAugust
2006, and jointly with the IEC on 214st August December 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.
· Proper diversion of surface runoff to the drainage system / sedimentation tank prior to discharge.
· Proper storage of stockpile and construction materials at designated storage area with cover to prevent soil being washed down into the drainage system.
The
record of the weekly site inspection findings is provided in Annex G.
4.2
Environmental Exceedances
During the reporting
period, there were totally seven four exceedances of Limit Level. Six of
which were noise exceedances of the lLimit lLevel
during restricted hours noise monitoring at CM1, CM2 and CM3 on 3rd,
17th, 24th and 31st 31st AugustDecember
2006.
Further to investigation and discussion with ER, the project-related works being undertaken during the
measurement period were located at a distance away (at least 180m) 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 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.
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, no environmental non-compliance was recorded.
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.
Additional
verification sampling at Site A as recommended in the approved CAR / RAP of
Site A & Site E would continue in January 2007.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 January 2007 is provided in Table 5.1 below:
Table 5.1 Proposed Noise Monitoring Schedule for September
January 2007
Date |
Noise
Monitoring Station |
5th
|
CM1, CM2 and CM3 |
11 |
|
17th
January 2007 (Wednesday) |
CM1, CM2 and CM3 |
23rd
January 2007
(Tuesday) |
CM1, CM2 and CM3 |
|
CM1, CM2 and CM3 |
There
was no environmental non-compliance attributable to the Project works during
reporting period.
There
were six
four records
of exceedances of the noise Limit Level during the reporting period. However, none of these are attributable to project works.
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.