PEAKO ENGINEERING CO., LTD
CONTRACT NO. HY/2002/08
Footbridge and Improvements to Ap Lei Chau
Bridge Road & Ap Lei Chau Drive
ANNUAL
ENVIRONMENTAL MONITORING
&
AUDIT REPORT
REPORT
NO. 01
(MAY
2003 – APR 2004)
Document
No. R/2647/014 Issue 1
May 2004
Babtie
Asia

CONTRACT NO. HY/2002/08
FOOTBRIDGE
AND IMPROVEMENTS TO AP LEI CHAU BRIDGE ROAD
AND AP
LEI CHAU DRIVE
ANNUAL
ENVIRONMENTAL MONITORING & AUDIT REPORT
REPORT
NO. 01
(MAY 2003 – APRIL 2004)
CONTENTS
EXECUTIVE SUMMARY
1.0
PROJECT INFORMATION
1.1 Background
1.2
Project
Organization & Contact Details of Key Personnel
1.5
Synopsis of
Work Undertaken during the Year
1.6
Project Area,
Sensitive Receivers & Monitoring Locations
1.7
Summary of EM&A
Requirements
2.0
IMPLEMENTATION STATUS
2.2 Advice on the Implementation Status of Environmental Protection
& Pollution Control / Mitigation Measures
3.0 MONITORING
RESULTS
3.1 Graphical Plots of the Monitored Parameters
3.2 Major Activities During the Year
4.0 SUMMARY OF NON-COMPLIANCE OF THE ACTION AND LIMIT LEVLER,
COMPLAINTS, NOTIFICATIONS OF SUMMONS AND SUCCESSFUL PROSECUTIONS
4.1 Non-compliance
of the Action and Limit Levels during the Year
4.1.1 Summary Record & Follow-up Actions
4.1.2 Review
of the reasons for and the implications of non-compliance
4.2 Written Complaints and Verbal Complaints
4.2.1 Summary Record of Complaints Received
4.3
Notifications
of summons and successful prosecutions for breaches
5.0
REVIEWS & COMMENTS
5.1
Validity
of EIA Report Predictions
5.2
Effectiveness and Efficiency
of the Mitigation Measures
5.3
EM & A Programme
APPENDICES
Appendix A Construction Programme
Appendix B Site Organization Chart
Appendix C Summary of EM & A Requirement
Appendix D The Project Area, Environmental
Sensitive Receivers and the Locations of the Monitoring Stations
Appendix E Weather Conditions during
the Year
Appendix F Graphical Plots of Trends of Monitored Parameters
Appendix G Statistics for
Environmental Complaints
EXECUTIVE SUMMARY
This is the first EM & A Report for the project of
Footbridge and Improvements to Ap Lei Chau Bridge Road & Ap Lei Chau Drive.
This report mainly presents
the EM & A works undertaken for the above project from 1 May 2003 to 30
April 2004 in accordance with the EM & A Manual and the Environmental
Permit (EP 130/2002) under the Appendix H of the Particular Specification.
Noise Level
During the reporting year, noise
monitoring was performed at four noise monitoring stations M1, M2, M3 and M4.
M1: The Ap
Lei Chau Baptist Kindergarten (NSR Ref. No. 10)
M2: The
Habour Mission Church and Yan Oi Kindergarten (NSR Ref. No. 12)
M3: The Hong
Kong True Light College (NSR Ref. No. 17)
M4: The Shan
On House (NSR Ref. No. 20)
Monitoring Stations M1, M2 and M3
are identified for educational uses at which the noise limit level is 70 dB(A)
during normal school hours and 65 dB(A) during examination period. M4 is
identified as domestic premise which noise limit level is 75 dB(A).
In the baseline noise monitoring,
the noise level recorded at M3, the Hong Kong True Light College, exceeded the
target limit level of 70 dB(A) prior to the commencement of construction works.
It was believed that the exceedance of noise level came from the traffic noise
generated from heavy goods vehicles and buses. In accordance with Section 3.7
of the Environmental Monitoring and Audit Manual, a new exceedance level which
incorporates the baseline noise and the construction noise shall be adopted for
accessing the noise impact to this noise monitoring station by the construction
works. The proposed new exceedance level for M3 has been submitted to EPD in
early May, it will be adopted as the new Limit Level for monitoring station M3
once EPD’s approval is received.
Complaint
log
Two verbal complaints and one written complaint were
received during the reporting year. Corresponding investigations and follow-up
actions were taken in compliance with the environmental standards stipulated in
the Environmental Monitoring and Audit Manual.
No notifications of summons, no successful prosecutions
were received during the year.
Review and
Comments
Noise
Impact Mitigation Measures
The mitigation measures mentioned in the EIA Report
generally help the Contractor reduce the noise level.
Air Impact
Mitigation Measures
The mitigation measures mentioned in the EIA Report
generally help the Contractor keep the air quality to a reasonable level.
Peako
Engineering Co. Ltd was commissioned by the Highways Departments to execute the
Project “Footbridge and Improvements to Ap Lei Chau Bridge Road and Ap Lei Chau
Drive”.
Babtie Asia
Ltd was employed by the Contractor to act as the Environmental Team for this
project. The Independent Environmental Checker is BMT Asia Pacific Limited.
The purpose
of this report is to document the Environmental Monitoring & Audit (EM
& A) works undertaken during the period between 1 May 2003 and 30 April
2004.
Titles,
names and contact telephone numbers of the key personnel of the captioned
project are tabulated below:
|
Title |
Name |
Contact Number |
|
Engineer’s Representative (Highways Department) |
Mr. W.
M. Chan |
2231
5722 |
|
EPD |
Mr.
Elvis Au |
2835
1964 |
|
Project Director (Contractor) |
Mr.
Ronnie Lo |
9144
8398 |
|
Project
Manager (Contractor) |
Mr. Steve C L Liu |
9551 1401 |
|
Site
Agent (Contractor) |
Mr. C.
P. Lam |
8206 8280 |
|
Environmental
Team Leader (Babtie
Asia Limited) |
Mr.
Mark Cheung |
2880
9788 |
|
Independent Environmental
Checker (BMT
Asia Pacific Limited) |
Ms.
Lyn Ip |
2241 9812 |

The project organization and lines
of communication with respect to the environmental monitoring works is shown
below.
This project involves four following stages;
·
Footbridge
Construction;
·
Retaining
Wall Construction;
·
Road
Construction; and
·
Drainage
Works
The anticipated construction period lasts 20 months. Night-time works
are not expected during the construction phase of the Project.
The latest construction programme is attached in Appendix A.
The site
organization chart is shown in Appendix B.
The works for this project are divided
into five major items
Item 1 – Junction
improvements to J/O Ap Lei Chau Bridge Road / Ap Lei Chau Drive, Ap Lei Chau
Drive / Ap Lei Chau Praya Road, and widening of Ap Lei Chau Drive.
Item 2 – Construction
/ modification of the footpaths and central reserves at Ap Lei Chau Bridge
Road, Ap Lei Chau Drive, and Lei Tung Estate Road.
Item 3 – Construction
/ modification of the retaining walls at Ap Lei Chau Bridge Road for the
construction of a staircase, a ramp and an elevated footpath.
Item 4
– Construction of a footbridge at Ap
Lei Chau Bridge Road.
Item 5 – Ancillary
works including slope works, landscaping works and drainage works.
Works
undertaken during the year are summarized as below:
·
Cut Slope
and Shotcreting at Ap Lei Chau Drive
·
Tree
Felling and Transplanting Works
·
Erection
of Temporary Works and Hoarding
·
Demolition
of Existing Counterfort Wall
·
Demolition
of Existing Caisson Wall at Ap Lei Chau Bridge Road Eastbound
·
Construction
of Retaining Wall
·
Utility
Diversion
·
Footway
and Carriageway Construction along Ap Lei Chau Drive
·
Erection
of Temporary Safety Fence along Ap Lei Chau Bridge Road
·
Installation
of concrete pipe
·
Soil Nail
Installation on Existing cut slope
·
Mini-pile
Drilling and Grouting Work
·
Pile Cap
Construction
·
Ramp
Construction
Layout
plan showing the project area, noise sensitive receivers (NSRs) and the
locations of the monitoring stations are shown in Appendix D.
The
construction noise monitoring stations are M1, M2, M3 and M4.
M1 is for the Ap Lei Chau
Baptist Kindergarten (NSR Ref. no.10). M2 is for the Harbour Mission Church and
Yan Oi Kindergarten (NSR Ref. no. 12). M3 is for the Hong Kong True Light
College (NSR Ref. no. 17). M4 is for the Shan On House (NSR Ref. no. 20).
It
is noted that the locations of the monitoring stations are the same as those
adopted in the Noise Baseline Monitoring.
Summary
of the EM&A Requirements is shown in Appendix C.
Impacts on the nearby sensitive receivers were
identified during various construction stages. Good site practice and
appropriate mitigation measures such as use of quiet plant, reducing percentage
on time, avoidance of simultaneous noisy activities have been recommended to
reduce the associated impacts.
According to the EIA report, the
following should be implemented during the construction period.
|
Location |
Reference Section |
Recommended Environmental Protection Measures |
Responsibility |
|
Construction
Noise Mitigation Measures |
|||
|
Various
Locations and work sites within the project limit |
Section
5.2.4 & 5.2.5 of EIA Report |
Reduce
the nuisance from Construction Noise ·
Adopt good site practice and proper site
management, e.g. plant shall be well maintained and mobile plant shall be
sited away from NSRs; ·
Use of quiet plant, such as dump truck, grader,
breaker and excavator, and working methods; ·
Control the number of equipment operating
concurrently; ·
Reduce the operating time of particular noisy
plant on site, e.g. shutting down machines between work periods; ·
Monitor noise levels from particularly noisy
activities; and if non-compliance with EIAO-TM standards is observed,
Contractor shall reduce the number of operating plant or re-adjust working
schedule to reduce the impact. |
Highways
Department and Contractor |
|
Location |
Reference Section |
Recommended Environmental Protection Measures |
Responsibility |
|
Construction
Dust Mitigation Measures |
|||
|
Various
Locations and work sites within the project limit |
Section
6.2.2 of EIA Report |
Reduce
the nuisance of Construction Dust ·
Follow the guidelines and regulatory requirements
of Air Pollution Control (Open Burning) Regulation and Air Pollution Control
(Construction Dust) Regulation; ·
Adopt appropriate environmental pollution control
measures on-site, such as, apply water sprays, use clean impervious sheeting
to cover dusty materials and set minimum practical height for dropping
materials. |
Highways
Department and Contractor |
The Contractor should use silencers or mufflers on
construction equipment such as pneumatic breaker and have air compressors
enclosed to avoid exceeding the noise limit and causing nuisance to the nearby
sensitive receivers.
Regular maintenance of the construction plant is
strongly encouraged to avoid black smoke and excessive noise production. The
machines and plant should be shut down or throttled down to a minimum when they
are in intermittent use.
The plant known to emit noise strongly in one
direction should be orientated to direct noise away from nearby noise sensitive
receivers. The mobile plants should be sited as far away from the noise
sensitive receivers as possible.
It is important to control the
simultaneous operation of the construction plant on site to avoid the potential
noise limit exceedance and nuisance to the nearby sensitive receivers
especially for those which are for educational purpose. The rock socket
excavation of the piling work shall be carried out after school hour to reduce
the nuisance to the nearby educational institutions.
The Contractor shall provide
temporary noise-insulating facilities such as hoarding, noise barrier at where
mostly affected by the Contractor’s construction activities.
The
Contractor shall note that the operation of Powered Mechanical Equipment in the
restricted hour without the valid Construction Noise Permit is considered as a
violation of current environmental regulations. The Contractor shall exercise a
tight control over its labours and its sub-contractor to prevent any breaches
of environmental regulations.
2.3
Mitigated Measures Taken by the Contractor During the
Year
Mitigation
measures exercised by the Contractor are summarized as follow:
Noise Mitigation Measures
·
Mufflers and silencers are mounted
on construction equipment when construction work is undertaking
·
Hoarding which acts as the
sound-insulating barrier is erected to surround the working area
·
Sound-insulating coverage board is
provided at the most affected area during the mini-pile drilling work
·
Rock socket excavation of
mini-pile construction is shifted to be carried out after school hour to reduce
the noise impact to the nearby education institutions
·
Simultaneous noisy activities are
avoided to be taken place
·
Construction plants are in intermittent
use shut down or throttled down to a minimum between work periods
·
Construction plants are
well-maintained on site
Dust Mitigation Measures
·
Sand heap is covered with
impervious tarpaulin when not used
·
Unpaved haul road is watered
regularly in the site
·
Effective water spraying system is
provided on site for dust suppression
·
Cover any dusty load on vehicle
before leaving the site
·
Water is sprayed at where the
concrete breaking taking place
Others
·
Direct site runoff to desilting
facilities such as sedimentation tank prior to the discharge to the stormwater
drainage system
·
Regularly clear the rubbish bin on
site
·
Enclose the working area where
mini-pile work or shotcreting work taking place
·
Accumulated stagnant water is
discharged to prevent the breeding of insects
·
Disused oil drum is transported
out of the site area
The
graphical presentations of the monitored parameters recorded in the past twelve
months are shown in Appendix G.
Works
undertaken during the year are summarized as below:
·
Cut Slope
and Slope Shotcreting at Ap Lei Chau Drive
·
Tree
Felling and Transplanting Works
·
Erection
of Temporary Works and Hoarding
·
Demolition
of Existing Counterfort Wall
·
Demolition
of Existing Caisson Wall at Ap Lei Chau Bridge Road Eastbound
·
Construction
of Retaining Wall
·
Utility
Diversion
·
Footway
and Carriageway Construction along Ap Lei Chau Drive
·
Erection
of Temporary Safety Fence along Ap Lei Chau Bridge Road
·
Installation
of concrete pipe
·
Soil Nail
Installation on Existing cut slope
·
Mini-pile
Drilling and Grouting Work
·
Pile Cap
Construction
·
Ramp
Construction
The weather conditions were
mainly sunny and did not affect the environmental monitoring works during the
reporting period. The weather conditions during the year are shown in the
Appendix E.
Other noise source included the noise from the
piling works at the site of Architectural Services Department inside the
monitoring station M3, the True Light College. Heavy traffic noise from Lei
Tung Estate Road also contributes noise impact to the monitoring station M3.
4.1.1 Summary Record
& Follow-up Actions
During the reporting year, all
measured noise levels were below the noise limit level at the monitoring
stations M1 and M4. Three of the measured noise levels at monitoring station M2
exceeded its limit level of 70 dB(A).
Based on the baseline noise monitoring results,
heavy traffic along Lei Tung Estate Road mainly contributes to the background
noise levels recorded in the vicinity of M3. As the baseline levels already
exceed the limit level for monitoring station M3, a new exceedance level which
incorporates the baseline noise level and construction noise level shall be
determined based on Section 3.7 of the EM&A Manual.
4.1.2 Review of the
reasons for and the implications of non-compliance
Reasons
leading to the non-compliance of noise limit level are summarized in below:
|
Date: |
Monitoring
Station |
Measured
Noise Level
dB(A) |
Reasons
account for the non-compliance & follow up actions |
|
17 May 2003 |
M2 |
74.0
dB(A) |
During these days, demolition of
the retaining wall CF1 was undertaken outside the monitoring station M2,
since there were no other noisy activities carried out by other parties, thus
the ET identified this as a non-compliance of noise limit level. Demolition works was stopped
immediately and ad hoc meeting was held amongst the principal and the
Contractor representative. The Contractor agreed to shift the working hours
of demolition works to non-school period. |
|
19 May 2003 |
M2 |
72.1
dB(A) |
|
|
24 May 2003 |
M2 |
72.7
dB(A) |
When the Contractor undertook
the demolition work at outside M2, at the same time, fixing works at the
external wall was undertaking by other parties inside the Harbour Mission
Church and Yan Oi Kindergarten. The exceedance was believed due to the
simultaneous machinery operation of fixing works and demolition work. Demolition works taken in the
remaining days was shifted to non-school period under the Engineer’s verbal
instruction. |
4.2.1 Summary Record of
Complaints Received
During
the reporting year, there was one written complaint and two verbal complaints
received in this project. Complaints’ details are shown as below:
Case 1
|
Received
date: |
19
May 2003 |
|
Complainant: |
The principal of the
Harbour Mission Church and Yan Oi Kindergarten |
|
Complaint Mode: |
Direct Contact with the
ER of the project |
|
Description of complaint: |
Noise Pollution due to
the Demolition Works at site |
|
Investigation: |
The ET found out the
Contractor was undertaking the demolition works of the existing retaining
wall outside the noise sensitive receiver M2 and it was believed the
complaint was solely due to noise generation by the Contractor’s construction
activities. The Contractor stopped
their works immediately once complaint was received. An ad hoc meeting was
held in the kindergarten amongst the principal and all relevant parties
including the ER and the Contractor representatives. |
|
Follow-up
Actions: |
The Contractor shifted the working
hour for the demolition works to non-school period to reduce the noise impact
to the kindergarten. Further meeting was held amongst
relevant parties on 27 May 2003, it was agreed the demolition works for the
lower 1.2m portion of the existing retaining wall could proceed within the
normal working hours, excluding between the period of 12:00am to 15:30pm
which is the sleeping time for the kindergarten children under the condition
that the equivalent noise level shall be below the contractual requirement of
70 dB(A). |
|
Recommended
Mitigation Measures: |
Silencers or mufflers on construction
equipment shall be utilized and properly maintained during the construction
works. Material stockpiles and other
structures shall be effectively utilised, where practicable, to screen noise
from on-site construction activities. Simultaneous operation of noisy plant
and equipment at places close to schools shall be avoided. The plant that is known to emit noise
strongly in one direction shall, where possible, be orientated to direct
noise away from nearby noise sensitive receivers. The working hours of the noisy plant
may be shifted to non-school hours to protect the sensitive receivers for
educational purposes. |
|
Status/
Remarks |
Closed. |
Case 2
|
Received
date: |
8 March 2004 |
|
Complainant: |
The principal of the Harbour Mission
Church and Yan Oi Kindergarten |
|
Complaint Mode: |
Written
Complaint |
|
Description of complaint: |
Noise
Pollution due to mini-pile drilling works at the Site |
|
Investigation: |
The ET believed that noise experienced
by the complainant came from the mini pile drilling work of the footbridge
construction at the Ap Lei Chau Bridge Road outside the HKHMC Yan Oi
Kindergarten. The ET instructed the Contractor to
undertake the additional noise monitoring on 11th March 2004, an
acceptable noise level of 69.3 dB(A) was recorded at noise monitoring station
at HKHMC Yan Oi Kindergarten (M2). |
|
Follow-up
Actions: Follow-up
Actions: |
An adhoc meeting was held between the kindergarten Principal and the
Contractor on mitigation measures of reducing the noise nuisance to the
kindergarten during the drilling works. Several mitigation measures were taken by the
Contractor including: Ø
Close all openings in the existing hoarding to
barricade the noise generated by the piling works. Ø
External coverage boards serving as noise
barriers will be provided in the most affected area in the kindergarten. Ø
The last 5m of rock socket excavation of piling
work was only carried out after the school hours. Noise measurements were carried out on 15th
and 16th March 2004 to assess the effectiveness of the
aforementioned mitigated measures and noise levels of 67.3 dB(A) and 65.6
dB(A) were recorded, respectively at M2, the HKHMC Yan Oi Kindergarten, which
satisfied the limit level of 70 dB(A) stipulated in the Environmental
Monitoring and Audit Manual. |
|
Recommended
Mitigation Measures: |
Material stockpiles and other structures shall be
effectively utilised, where practicable, to screen noise from on-site construction
activities. The working hours of the noisy plant may be
shifted to non-school hours to protect the sensitive receivers for
educational purposes. |
|
Status/
Remarks |
Closed. |
Case 3
|
Received
date: |
12 April 2004 |
|
Complainant: |
A Pedestrian |
|
Complaint Mode: |
Verbal
Complaint |
|
Description of complaint: |
Noise Pollution due to the removal of
mini-pile loading test set up during the Easter Holiday |
|
Investigation: |
The ET found that a Powered Mechanical Equipment was illegally
operated by the Sub-Contractor for the removal of the pile loading test
set-up in restricted hours without a valid Construction Noise Permit. |
|
Follow-up
Actions: |
The Contractor was reminded that the
use of PME in the restricted hour without the Construction Noise Permit is unacceptable.
|
|
Recommended
Mitigation Measures: |
|
|
Status/ Remarks |
Closed. |
The following table shows
the summary for all the complaints received since the commencement of the
Contract.
|
TOTAL NO. OF COMPLAINT |
NO. OF COMPLAINT
RECEIVED WITHIN REPORTING PERIOD |
NO. OF COMPLAINT THAT IS
STILL UNDER INVESTIGATION |
NO. OF CLOSED COMPLAINT |
|
3 |
0 |
0 |
3 |
The statistics for environmental complaint and
complaint log during the reporting year are shown in Appendix G.
During the year, there were no
notifications of summons and successful prosecutions for breaches of any environmental
laws.