TABLE OF CONTENTS
Page
1.4 Summary of Construction Works
1.5 Summary of EM&A Programme
Requirements
2.4 Monitoring Parameters, Frequency
and Duration
2.6 Monitoring Schedule for the
Reporting Period
4.3 Biopiling and Cement
Solidification / Stabilization Progress
4.4 Monitoring Testing Results
5 ENVIRONMENTAL SITE
INSPECTION AND AUDIT
5.2 Advice on the Solid and Liquid
Waste Management Status
5.3 Environmental Licenses and
Permits
5.4 Implementation Status of
Environmental Mitigation Measures
5.5 Summary of Exceedances of the
Environmental Quality Performance Limit
5.6 Summary of Complaints,
Non-compliances, Notification of Summons and Successful Prosecutions
6.1 Construction Programme for the
Coming Months
6.2 Key Issues for the Coming Month
6.3 Monitoring Schedule for the
Coming Month
7 comments,
Recommendations and ConclusionS
7.1 Comments on Mitigation Measures
7.2 Recommendations on EM&A
Programme
List of Tables
Table 1.1 Contact Information of Key Personnel
Table 2.1 Noise Monitoring Equipment
Table 2.2 Locations of Impact Noise Monitoring Stations
Table 2.3 Noise Monitoring Parameters, Frequency and Duration
Table 2.4 Summary of Noise Monitoring Results in the Reporting
Period
Table 4.1 Summary of Progress of Excavation and Verification
Sampling
Table 4.2 Results of Spot-check Samples and their Corresponding
Verification Samples
Table 4.3 Test Results for Cement Solidification and
Stabilization Treated Samples
Table 4.4 Results of QA/QC Samples Receive in February 2014
Table 5.1 Summary of Environmental Licensing and Permit Status
List of Figures
Figure
2 Noise Monitoring Locations
Figure 3 Environmental Complaint Handling Procedure
Figure
4 Locations of Contamination
Zones
Figure 5 Locations of Confirmatory Sampling
(Zones R5 & R6)
Figure 6 Locations of Confirmatory Sampling
(Zones R1 & R7)
Figure 7 Locations of Confirmatory Sampling
(Zones R2 & R3)
Figure 8 Locations of Confirmatory Sampling
(Zones R4 & R8)
Figure
9 Locations of Confirmatory
Sampling (Zone A1)
Figure 10 Locations of Confirmatory Sampling
(Zones A2, A3, A4 & A5)
Figure
11 Locations of Confirmatory
Sampling (Zones T32C, T32D, T32E, T35C & T36A)
Figure
12 Locations of Confirmatory
Sampling (Zones T19A, T22BA, T22BB)
Figure
13 Locations of Confirmatory
Sampling (Zone T32E)
Figure
14 Locations of Confirmatory
Sampling (Zone T35C)
List of Appendices
Appendix A Project
Organization Structure
Appendix B Construction
Programme
Appendix
C Implementation Schedule of
Environmental Mitigation Measures (EMIS)
Appendix
D Summary of Action and Limit
Levels
Appendix E Calibration
Certificates of Monitoring Equipments
Appendix F EM&A
Monitoring Schedules
Appendix G Impact
Daytime Construction Noise Monitoring Results and their Graphical Presentation
Appendix I Site Inspection Summaries
Appendix J Cumulative
Statistics on Complaints, Notifications of Summons and Successful Prosecutions
Appendix K Laboratory
Testing Reports
Appendix L Summary Table of Testing Results
The proposed “Yau Tong Bay – Decommissioning of Shipyard Sites” (hereinafter referred to as “the Project”) is a Designated Project under the Environmental Impact Assessment Ordinance (Cap. 499) Schedule 2 and is governed by the Environmental Permit No. EP-409/2010. The Project aims to demolish the past and existing shipyards and their building structures and marine structures and decontaminate identified contaminated spots.
The demolition works of the Project commenced on 21 November 2011 and was completed in September 2012. The impact Environmental Monitoring and Audit (hereinafter referred to as “EM&A”) programme for the Project commenced on 21 November 2011. The EM&A works was suspended from November 2012 for the captioned Project and the EM&A works has been resumed on 28 October 2013. The impact EM&A programme includes daytime construction noise and water quality monitoring, soil remediation works monitoring and auditing and site auditing. The remediation method statement was approved by the EPD on 20 December 2013. The soil remediation works commenced on 23 December 2013.
This report documents the findings of EM&A works conducted in the period between 1 and 28 February 2014.
As informed by the Contractor, the major construction activities carried
out in
the reporting period were
excavation of contaminated soil in Zones T32E (outer), T36A and R8, backfilling
Zones R2, R4, A1, T32E (inner) and T36A, formation of biopiles and cement
solidification treatment for Zone T36A.
A summary of
monitoring and audit activities conducted in the reporting period is listed
below:
Daytime noise
monitoring |
2 sessions |
Water quality
monitoring |
0 session |
Environmental
site inspection |
4 sessions |
Breaches of Action and Limit Levels for Daytime Construction Noise
No Action Level exceedance was recorded since no construction noise related complaint was received in the reporting period.
No Limit Level exceedance of construction noise was recorded in the reporting period.
Breaches of Action and Limit
Levels for Water Quality
Water quality monitoring was not conducted in the reporting period as the demolition of marine structures has not yet commenced. No Action/Limit Level exceedance of water quality was recorded in the reporting period.
Environmental Complaint,
Non-compliance, Notification of Summons and Successful Prosecution
No complaint, non-compliance, notification of summons and successful
prosecution was received in the reporting period.
Reporting Change
There was no reporting change required in the reporting period.
Future Key Issues
Excavation
of contaminated soil will continue to take place in March 2014.
「油塘灣–船廠拆卸工程」(以下簡稱「本工程項目」)是一項被臚列於環境影響評估條例(第 499章)附表2中的指定工程項目並受到環境許可證編號EP-409/2010所管制。本工程項目的主要目的是要拆除位於油塘灣的舊有和現有的船廠及其建築物和海事結構,以及處理指定的已受污染點。
本工程項目已於二零一一年十一月二十一日峻工並於二零一二年九月完工。本工程項目的施工期間環境監察及審核計劃亦由二零一一年十一月二十一日開始。由二零一二年十一月起,本工程項目之施工期間環境監察與審核工作暫停,並於二零一三年十月二十八日恢復。施工期間環境監察與審核計劃包括:日間建築噪音監測,水質監測,已受污染泥復育工作的監察與審核及工地審核巡查。環保署在二零一三年十二月二十日批准了土地整治方法聲明。土壤修復工程於二零一三年十二月二十三日開始。
本報告記錄了於二零一四年二月一日至二月二十八日期間所進行的環境監察與審核工作。
根據承建商提供的資料,在上述的期間的主要建築活動為在區域T32E(外部)、T36A和R8污染土壤的挖掘、在區域R2、R4、A1、T32E(內部)和T36A的回填、生物堆的形成以及在區域T36A的水泥固化處理。
在上述的期間有下列次數的監察及審核活動進行:
日間建築噪音監測 2次
水質監測 0次
環境巡查 4次
違反監測標準
日間建築噪音
在上述的期間沒有收到有關建築噪音的投訴,所以噪音監測結果皆符合行動水平。
在上述的期間的所有日間建築噪音監測結果皆符合極限水平。
水質
因為相關的海事結構拆除工程仍未開始,故沒有水質監測在上述的期間進行。因此,沒有違反水質行動水平和極限水平的記錄。
有關收到的環境的投訴,傳票及檢控
在上述的期間沒有收到有關環境的投訴,傳票及檢控。
報告修訂
本報告期間並沒有修訂報告。
預計要注意的事項
污染土壤的挖掘將在2014年3月繼續。
1.1.1.
The
Project Site of “Yau Tong Bay-Decommissioning of Shipyard Sites” (hereinafter
referred to as “the Project”) is located
along the shore of Yau Tong Bay (which is also known as Kwun Tong Tsai Wan) in
East Kowloon within the Kwun Tong District and the Project Site together with
its adjacent land is zoned Comprehensive Development area (“CDA”) on the
Approved Cha Kwo Ling, Yau Tong, Lei Yue Mun Outline Zoning Plan (OZP) No.
S/K15/19. It faces Victoria Harbour to
the southwest and is bounded by the Eastern Harbour Crossing Ventilation
Building to the west, Cha Kwo Ling Road to the north and east, and Ko Fai Road
to the south. The site is also adjacent
to the former Yau Tong Industrial Area, which is at present mainly occupied by
obsolete industrial buildings.
1.1.2.
The
Project is a designated project and is governed by the Environmental Permit No.
EP-409/2010 (hereinafter referred to as “the EP”).
1.1.3.
Major works to be undertaken in the Project
include:-
Demolition of past and existing shipyard and building structures;
Demolition of marine structure of shipyards; and
Decontamination of identified contaminated spots.
1.1.4.
For the decommissioning of past and existing
shipyard lots, there is a total of 39 Marine Lots along the shore of Yau Tong
Bay are under the control of the Project Proponent (Main Wealth Development
Limited) and covered in this Project.
These 39 lots (or the ‘concerned lots’) ,with a total area of over 1
hectare (ha), as listed below and highlighted in Figure 1, are hereinafter referred to as the ‘Project Site’. The land uses for the Project Site had been
industrial and various land uses including shipyards, timber yards, sawmills and concrete batching plant.
YTML No. 1
YTMLs No. 5-14
YTML No. 15
YTMLs No. 19-24
YTMLs No. 27-38
YTMLs No. 41-46
YTML No. 54
1.1.5.
Main Wealth Development Limited (the Project
Proponent) has commissioned AECOM Asia Company Limited as the Engineer of the
Project and Kin Wing Construction Co., Ltd was commissioned as the
Decontamination Contractor of the Project (hereafter referred to as “the
Contractor”).
1.1.6.
AECOM Asia Company Limited was appointed to
undertake the Environmental Team (hereafter referred to as “ET”) services for
implementation of all the Environmental Monitoring and Audit (hereafter
referred to as “EM&A”) works under the Project. Mott MacDonald Hong Kong
Limited and Nature & Technologies (HK) Limited act as the Independent
Environmental Checker (hereafter referred to as “IEC”) and Independent
Environmental Auditor (hereafter referred to as “IEA”) for the Project respectively.
1.1.7.
According
to the updated programme, the demolition works of the
Project commenced on 21 November 2011. Hoarding and demolition works for the Project were completed in September
2012. The remediation method statement was approved by the EPD on 20
December 2013. The soil remediation works commenced on 23 December 2013.
1.1.8.
In accordance with the updated Environmental
Monitoring and Audit Manual (hereinafter referred to as “the EM&A Manual”) of the Project,
there is a need of an impact EM&A programme includes daytime
construction noise and water quality monitoring, soil
remediation works monitoring and auditing and site auditing. The impact EM&A Programme for the Project
commenced on 21 November 2011. The EM&A works was suspended from
November 2012 for the captioned Project and the EM&A works has been resumed
on 28 October 2013.
Table 1.1 Contact Information of Key Personnel
Party |
Name |
Telephone |
Fax |
Project
Proponent (Main Wealth Development Limited) |
Gregory Chan |
2908 8679 |
2562 0029 |
Engineer (AECOM Asia Co. Ltd.) |
Jeremy Yuen |
3922 9000 |
3922 9797 |
Decontamination Contractor (Contractor) (Kin Wing Construction Co., Ltd) |
Lee Kam Hung |
2717 9139 |
2725 9316 |
Independent Environmental Checker (IEC) (Mott MacDonald Hong Kong Limited) |
Terence Kong |
2828 5919 |
2827 1823 |
Independent Environmental Auditor (IEA) (Nature & Technologies (HK) Limited) |
Gabriel Lam |
2877 3122 |
2511 0922 |
Environmental
Team Leader (ETL) (AECOM Asia Co. Ltd.) |
Y T Tang |
3922 9393 |
3922 9797 |
-
All monitoring parameters;
-
Monitoring schedules for the reporting month
and forthcoming months;
-
Action and Limit levels for all environmental
parameters;
-
Event / Action Plan;
-
Environmental mitigation measures, as
recommended in the Project EIA study final report; and
-
Environmental requirement in contract
documents.
Table 2.1 Noise
Monitoring Equipment
Equipment |
Brand and Model |
Integrated Sound Level
Meter |
Rion NL-31 (00320528);
B&K 2270 (2644597) |
Acoustic Calibrator |
Rion NC-73 (10307223);
Rion NC-73 (10186482) |
Table 2.2 Locations
of Impact Noise Monitoring Stations
Monitoring Station |
Location |
Description |
NM1 |
Yau Lai Estate Hong
Lai House |
1m from the exterior
of the roof top façade of the building |
NM2 |
S.K.H. Yau Tong Kei
Hin Primary School |
1m from the exterior
of the roof top façade of the building |
NM3 |
C.C.C. Kei Faat
Primary School (Yau Tong) |
1m from the exterior
of the roof top façade of the building |
Table 2.3 Noise Monitoring Parameters, Frequency
and Duration
Parameter |
Frequency and Duration |
30-mins measurement at each monitoring
station between 0700 and 1900 on normal weekdays. Leq, L10
and L90 would be recorded. |
At least once
per two weeks |
(a)
Façade measurements were made at all monitoring
locations.
(b)
The battery condition was checked to ensure the
correct functioning of the meter.
(c)
Parameters such as frequency weighting, the time
weighting and the measurement time were set as follows:-
(i)
frequency weighting: A
(ii)
time weighting: Fast
(iii)
time measurement: Leq(30-minutes) during
non-restricted hours i.e. 07:00 – 1900 on normal weekdays; Leq(5-minutes)
during restricted hours i.e. 19:00
– 23:00 and 23:00 – 07:00 of normal weekdays, whole day of Sundays and Public
Holidays
(d)
Prior to and after each noise measurement, the
meter was calibrated using the acoustic calibrator for 94dB(A)
at 1000 Hz. If the difference in the
calibration level before and after measurement was more than 1 dB(A), the measurement would be considered invalid and
repeat of noise measurement would be required after re-calibration or repair of
the equipment.
(e)
During the monitoring period, the Leq, L10
and L90 were recorded. In
addition, site conditions and noise sources were recorded on a standard record
sheet.
(f)
Noise measurement was paused during periods of high
intrusive noise (e.g. dog barking, helicopter noise) if possible. Observations
were recorded when intrusive noise was unavoidable.
(g)
Noise monitoring was cancelled in the presence of
fog, rain, wind with a steady speed exceeding 5m/s, or wind with gusts
exceeding 10m/s.
(a)
The microphone head of the sound level meter was
cleaned with soft cloth at regular intervals.
(b)
The meter and calibrator were sent to the supplier or
HOKLAS laboratory to check and calibrate at yearly intervals.
(c)
Calibration certificates of the sound level meters
and acoustic calibrators are provided in Appendix
E.
Table 2.4 Summary
of Noise Monitoring Results in the Reporting Period
|
Average, dB(A), Leq (30 mins) |
Range, dB(A), Leq
(30 mins) |
Limit Level, dB(A), Leq
(30 mins) |
NM1 |
58.5 |
55.2 – 60.4 |
75 |
NM2 |
63.2 |
61.0 – 64.7 |
70# |
NM3 |
64.1 |
61.3 – 65.8 |
70/65# |
# Limit
Level of 70dB(A) applies to education institutes while
65dB(A) applies during school examination period.
4.2.3 Independent Environmental Auditor (IEA) has conducted spot check sampling on 24 February 2014 at zone T32E (verification samples at base). The result has not been received by the time of reporting and thus will be included in the next monthly report. The testing results of the IEA samples and the corresponding verification samples collected since December 2013 are summarized in Table 4.2 and are found to be in order with the results of the Contractor.
Table 4.1 Summary
of Progress of Excavation and Verification Sampling
Zone ID |
Status of Excavation |
Verification samples |
Additional samples |
Sampling Status |
Testing Result^ (Pass/Fail) |
T19A |
Not Excavated |
Top |
- |
- |
- |
T19A.1/SW (Sidewall) |
- |
ü |
Pass |
||
T19A.2/SW (Sidewall) |
T19A.2.1/SW (Sidewall) |
ü |
Pass |
||
T19A.3/SW (Sidewall) |
T19A.3.1/SW (Sidewall) |
ü |
Pass |
||
T19A.4/SW (Sidewall) |
T19A.4.1/SW (Sidewall) |
ü |
Pass |
||
T19A.4.2/SW (Sidewall) |
|||||
T19A/B (Base) |
- |
ü |
Pass |
||
T19A/B1 (Base) |
- |
ü |
Pass |
||
T22BA |
Not Excavated |
Top |
- |
- |
- |
T22BA.1/SW (Sidewall) |
- |
ü |
Pass |
||
T22BA.2/SW (Sidewall) |
- |
ü |
Pass |
||
T22BA.3/SW (Sidewall) |
T22BA.3.1/SW (Sidewall) |
ü |
Pass |
||
T22BA.3.2/SW (Sidewall) |
|||||
T22BA.3.3/SW (Sidewall) |
|||||
T22BA.3.4/SW (Sidewall) |
|||||
T22BA.4/SW (Sidewall) |
T22BA.4.1/SW (Sidewall) |
ü |
Pass |
||
T22BA/B (Base) |
- |
ü |
Pass |
||
T22BA/B1 (Base) |
T22BA/B1.1 (Base) |
ü |
Pass |
||
T22BA/B1.2 (Base) |
|||||
T22BB |
Not Excavated |
Top |
- |
- |
- |
T22BB.1/SW (Sidewall) |
- |
ü |
Pass |
||
T22BB.2/SW (Sidewall) |
- |
ü |
Pass |
||
T22BB.3/SW (Sidewall) |
T22BB.3.1/SW (Sidewall) |
ü |
Pass |
||
T22BB.3.2/SW (Sidewall) |
|||||
T22BB.4/SW (Sidewall) |
- |
ü |
Pass |
||
T22BB/B (Base) |
- |
ü |
Pass |
||
T22BB/B1 (Base) |
- |
ü |
Pass |
||
T32C |
Excavation in progress |
Top |
- |
- |
- |
T32C.1/SW (Sidewall) |
T32C.1.1/SW (Sidewall) |
ü |
Pass |
||
T32C.2/SW (Sidewall) |
- |
ü |
Pass |
||
T32C.3/SW (Sidewall) |
- |
ü |
Pass |
||
T32C.4/SW (Sidewall) |
T32C.4.1/SW (Sidewall) |
ü |
Pass |
||
T32C/B (Base) |
- |
ü |
Pass |
||
T32C/B1 (Base) |
- |
ü |
Pass |
||
T32D |
Not Excavated |
T32D/T (Top) |
- |
ü |
Pass |
T32D.1/SW (Sidewall) |
- |
ü |
Pass |
||
T32D.2/SW (Sidewall) |
- |
ü |
Pass |
||
T32D.3/SW (Sidewall) |
- |
ü |
Pass |
||
T32D.4/SW (Sidewall) |
- |
ü |
Pass |
||
T32D/B (Base) |
- |
ü |
Pass |
||
T32E (PCB Contaminated Zone) |
Excavation Completed |
Top |
- |
- |
- |
T32E.1A/SW (Sidewall) |
- |
ü |
Pass |
||
T32E.2A/SW (Sidewall) |
- |
ü |
Pass |
||
T32E.3A/SW (Sidewall) |
T32E.3A.1/SW (Sidewall) |
ü |
Pass |
||
T32E.3A.2/SW (Sidewall) |
|||||
T32E.4A/SW (Sidewall) |
T32E.4A.1/SW (Sidewall) |
ü |
Pass |
||
T32E.4A.2/SW (Sidewall) |
|||||
T32E.4A.3/SW (Sidewall) |
|||||
T32E/B (Base) |
- |
ü |
Pass |
||
T32E |
Excavation Completed |
Top |
- |
- |
- |
T32E.1/SW – T32E.58/SW (Sidewall) |
T32E.(10,11,15-19,25,26,30-32,34,37) .1
(Sidewall) |
ü |
Pending |
||
T32E.(11,15-17,26,30-32,34) .2 (Sidewall) |
|||||
T32E/B/1-14
(Base) |
- |
ü |
Pending |
||
T32E/B/15-18
(Base) |
- |
ü |
Pending |
||
T35C |
Excavation Completed |
Top |
- |
- |
- |
T35C.1/SW – T35C.77/SW (Sidewall) |
- |
ü |
Pass |
||
T35C.B1 – T35C.B26(Base) |
T35C.B5.1 |
ü |
Pass |
||
T35C.B27 – T35C.B47(Base) |
- |
ü |
Pending |
||
T35C.B48 – T35C.B66(Base) |
- |
ü |
Pending |
||
T36A |
Excavation Completed |
Top |
- |
- |
- |
T36A.1/SW (Sidewall) |
- |
ü |
Pass |
||
T36A.2/SW (Sidewall) |
- |
ü |
Pass |
||
T36A.3/SW (Sidewall) |
- |
ü |
Pass |
||
T36A.4/SW (Sidewall) |
- |
ü |
Pass |
||
T36A/B (Base) |
- |
ü |
Pass |
||
T36A/B1 (Base) |
- |
ü |
Pass |
||
A1 |
Excavation Completed |
Top |
- |
- |
- |
A1.1-A1.2/SW (Sidewall) |
- |
ü |
Pass |
||
A1.1-A1.4/SW (Sidewall) |
- |
ü |
Pass |
||
A1.2-A1.3/SW (Sidewall) |
- |
ü |
Pass |
||
A1.3-A1.4/SW (Sidewall) |
- |
ü |
Pass |
||
A1/B (Base) |
- |
ü |
Pass |
||
A2 |
Excavation Completed |
A2/T (Top) |
- |
ü |
Pass |
A2.1-A2.2/SW (Sidewall) |
A2.1-A2.2.1/SW (Sidewall) |
ü |
Pass |
||
A2.1-A2.4/SW (Sidewall) |
- |
ü |
Pass |
||
A2.2-A2.3/SW (Sidewall) |
- |
ü |
Pass |
||
A2.3-A2.4/SW (Sidewall) |
- |
ü |
Pass |
||
A2/B (Base) |
- |
ü |
Fail* |
||
A3 |
Not excavated |
Top |
- |
- |
- |
Sidewall |
- |
O |
No Sampling |
||
Base |
- |
O |
No Sampling |
||
A4 |
Not excavated |
A4/T (Top) |
- |
ü |
Pass |
A4.1-A4.2/SW (Sidewall) |
- |
ü |
Pass |
||
A4.1-A4.4/SW (Sidewall) |
- |
ü |
Pass |
||
A4.2-A4.3/SW (Sidewall) |
A4.2-A4.3.1/SW (Sidewall) |
ü |
Pass |
||
A4.3-A4.4/SW (Sidewall) |
A4.3-A4.4.1/SW (Sidewall) |
ü |
Fail |
||
A4.3-A4.4.2/SW (Sidewall) |
|||||
A4.3-A4.4.3/SW (Sidewall) |
|||||
A4.3-A4.4.4/SW (Sidewall) |
O |
No Sampling |
|||
A4/B (Base) |
- |
ü |
Pass |
||
A5 |
Not excavated |
A5/T (Top) |
- |
ü |
Pass |
A5.1-A5.2/SW (Sidewall) |
A5.1-A5.2.1/SW (Sidewall) |
ü |
Pass |
||
A5.1-A5.2.2/SW (Sidewall) |
|||||
A5.1-A5.4/SW (Sidewall) |
A5.1-A5.4.1/SW (Sidewall) |
ü |
Fail |
||
A5.1-A5.4.2/SW (Sidewall) |
|||||
A5.1-A5.4.3/SW (Sidewall) |
|||||
A5.1-A5.4.4/SW (Sidewall) |
O |
No Sampling |
|||
A5.2-A5.3/SW (Sidewall) |
A5.2-A5.3.1/SW (Sidewall) |
ü |
Pass |
||
A5.3-A5.4/SW (Sidewall) |
- |
ü |
Pass |
||
A5/B (Base) |
- |
ü |
Pass |
||
R1 |
Excavation Completed |
Top |
- |
- |
- |
R1.1-R1.2/SW (Sidewall) |
- |
ü |
Pass |
||
R1.1-R1.4/SW (Sidewall) |
- |
ü |
Pass |
||
R1.2-R1.3/SW (Sidewall) |
- |
ü |
Pass |
||
R1.3-R1.4/SW (Sidewall) |
- |
ü |
Pass |
||
R1/B (Base) |
- |
ü |
Pass |
||
R2 |
Excavation Completed |
Top |
- |
- |
- |
R2.1-R2.2/SW (Sidewall) |
- |
ü |
Pass |
||
R2.1-R2.4/SW (Sidewall) |
- |
ü |
Pass |
||
R2.2-R2.3/SW (Sidewall) |
R2.2-R2.3.1/SW (Sidewall) |
ü |
Pass |
||
R2.2-R2.3.2/SW (Sidewall) |
|||||
R2.3-R2.4/SW (Sidewall) |
- |
ü |
Pass |
||
R2/B (Base) |
- |
ü |
Pass |
||
R3 (0-1m below ground surface) |
Not excavated |
Top |
- |
- |
- |
R3.1-R3.2/SW (Sidewall) |
- |
ü |
Pass |
||
R3.1-R3.4/SW (Sidewall) |
- |
ü |
Pass |
||
R3.2-R3.3/SW (Sidewall) |
- |
ü |
Pass |
||
R3.3-R3.4/SW (Sidewall) |
- |
ü |
Pass |
||
R3/B (Base) |
- |
ü |
Pass |
||
R3 (1-3.95m below ground surface) |
Not excavated |
Top |
- |
- |
- |
R3.1-R3.2/SW (Sidewall) |
- |
ü |
Pass |
||
R3.1-R3.4/SW (Sidewall) |
- |
ü |
Pass |
||
R3.2-R3.3/SW (Sidewall) |
- |
ü |
Pass |
||
R3.3-R3.4/SW (Sidewall) |
- |
ü |
Pass |
||
R3/B (Base) |
- |
ü |
Pending |
||
R4 |
Excavation Completed |
Top |
- |
- |
- |
R4.1-R4.2/SW (Sidewall) |
- |
ü |
Pass |
||
R4.1-R4.4/SW (Sidewall) |
- |
ü |
Pass |
||
R4.2-R4.3/SW (Sidewall) |
- |
ü |
Pass |
||
R4.3-R4.4/SW (Sidewall) |
- |
ü |
Pass |
||
R4/B (Base) |
- |
ü |
Pass |
||
R5 |
Excavation Completed |
Top |
- |
- |
- |
R5.1-R5.2/SW (Sidewall) |
- |
ü |
Pass |
||
R5.1-R5.4/SW (Sidewall) |
R5.1-R5.4.1/SW (Sidewall) |
ü |
Pass |
||
R5.2-R5.3/SW (Sidewall) |
- |
ü |
Pass |
||
R5.3-R5.4/SW (Sidewall) |
- |
ü |
Pass |
||
R5/B (Base) |
- |
ü |
Pass |
||
R6 |
Not excavated |
R6/T (Top) |
- |
ü |
Pass |
R6.1-R6.2/SW (Sidewall) |
- |
ü |
Pass |
||
R6.1-R6.4/SW (Sidewall) |
- |
ü |
Pass |
||
R6.2-R6.3/SW (Sidewall) |
- |
ü |
Pass |
||
R6.3-R6.4/SW (Sidewall) |
- |
ü |
Pass |
||
R6/B (Base) |
- |
O |
No Sampling |
||
R7 |
Not excavated |
Top |
- |
O |
No Sampling |
Sidewall |
- |
O |
No Sampling |
||
Base |
- |
O |
No Sampling |
||
R8 |
Excavation Completed |
R8/T (Top) |
R8/T.1 (Top) |
ü |
Pass |
R8.1-R8.2/SW (Sidewall) |
- |
ü |
Pass |
||
R8.1-R8.4/SW (Sidewall) |
- |
ü |
Pass |
||
R8.2-R8.3/SW (Sidewall) |
- |
ü |
Pass |
||
R8.3-R8.4/SW (Sidewall) |
- |
ü |
Pass |
||
R8/B (Base) |
- |
ü |
Pass |
||
UG Tank |
Tank Removed |
Top |
- |
- |
- |
U01/SW (Sidewall) |
- |
ü |
Pass |
||
U02/SW (Sidewall) |
- |
ü |
Pass |
||
U03/SW (Sidewall) |
- |
ü |
Pass |
||
U04/SW (Sidewall) |
- |
ü |
Pass |
||
U05/B (Base) |
- |
ü |
Pass |
Note:
ü: Sampled
O: Not sampled yet
- : Sampling not required
^: Where applicable, the indicated testing results represent the status
of the most recent additional sample taken for the same location.
*: Additional base sampling for A2 is not required as that part of soil
is included in A3.
Table 4.2 Results
of Spot-check Samples and their Corresponding Verification Samples
Parameters |
Lead (Dutch B Standard) |
TPH (Dutch B Standard) |
PCR(RBRG) |
TCLP |
|||||||
Lead |
C6-C9 |
C10-C14 |
C15-28 |
C29-C36 |
Total TPH |
C9-C16 |
C17-C35 |
Lead |
|||
Limit of Reporting (LOR) (mg/kg) |
1 |
2 |
50 |
100 |
100 |
252 |
200 |
500 |
0.1 |
||
Standard limits(mg/kg) |
150 |
- |
- |
- |
- |
1,000 |
2,240 |
10,000 |
0.75 |
||
Zone ID |
Sampling ID |
Sampling Date |
|
||||||||
T22BA |
T22BA.4.1/SW/ 0.75 |
4-Dec-14 |
131 |
- |
- |
- |
- |
- |
- |
- |
- |
T22BA.4.1/ SW/0.75/IEA |
4-Dec-14 |
112 |
- |
- |
- |
- |
- |
- |
- |
- |
|
R3 |
R3.1-R3.2/ SW/2.475 |
19-Dec-13 |
- |
- |
- |
- |
- |
- |
299 |
9,030 |
- |
R3.1-R3.2/ SW/2.475/IEA |
19-Dec-13 |
- |
- |
- |
- |
- |
- |
266 |
9,270 |
- |
|
T35C |
T35C.56/SW/1.25 |
9-Jan-14 |
- |
<2 |
<50 |
<100 |
<100 |
<252 |
- |
- |
- |
T35C.56/ SW/1.25/IEA |
9-Jan-14 |
- |
<2 |
<50 |
<100 |
<100 |
<252 |
- |
- |
- |
|
R5 |
R5/TCLP |
22-Jan-14 |
- |
- |
- |
- |
- |
- |
<0.1 |
<0.1 |
<0.1 |
R5/TCLP/IEA |
22-Jan-14 |
- |
- |
- |
- |
- |
- |
<0.1 |
<0.1 |
<0.1 |
Table 4.3 Test
Results for Cement Solidification and Stabilization Treated Samples
Parameter |
TCLP (Lead) |
UCS |
|
Unit |
mg/kg |
kPa |
|
Limit of
Reporting (LOR) |
0.1 |
0.5 |
|
Target |
<0.75 |
>1 |
|
Sample ID |
Date of Sampling |
|
|
A1/TCLP |
21/1/2014 |
<0.1 |
3.5 |
A1/TCLP.1 |
21/1/2014 |
<0.1 |
1.7 |
R5/TCLP |
22/1/2014 |
<0.1 |
2.5 |
R5/TCLP.1 |
22/1/2014 |
<0.1 |
2.5 |
4.4.2 Among the 106 results received in February, exceedance of relevant standards was found in 28 samples. These 28 samples are additional samples taken for previous exceeding results in zones A4, A5, T32E and T35C. The sampling and reporting status of the verification samples are indicated in Table 4.1. The testing results are summarized in the table of Appendix L, and the laboratory testing reports are filed in Appendix K.
Table 4.4 Results
of QA/QC Samples Receive in February 2014
Parameter |
Lead |
Copper |
TPH C6-C9 |
TPH C10-C14 |
TPH C15-C28 |
TPH C29-C36 |
|
Limit of
Reporting (LOR) (mg/kg) |
1 |
1 |
2 |
50 |
100 |
100 |
|
RBRGs (Urban
Residential) (mg/kg) |
150 |
100 |
- |
- |
- |
- |
|
Sample ID |
Date of
Sampling |
|
|
|
|
|
|
FB12 |
20/1/2014 |
<1 |
<1 |
<20 |
<50 |
<100 |
<50 |
EB12 |
20/1/2014 |
<1 |
<1 |
<20 |
<50 |
<100 |
<50 |
FB13 |
20/1/2014 |
|
|
<20 |
<50 |
<100 |
<50 |
EB13 |
20/1/2014 |
|
|
<20 |
<50 |
<100 |
<50 |
FB14 |
24/01/2014 |
|
|
<20 |
<50 |
<100 |
<50 |
EB14 |
24/01/2014 |
|
|
<20 |
<50 |
<100 |
<50 |
FB15 |
24/01/2014 |
|
|
<20 |
<50 |
<100 |
<50 |
EB15 |
24/01/2014 |
|
|
<20 |
<50 |
<100 |
<50 |
FB16 |
17/02/2014 |
|
|
<20 |
<50 |
<100 |
<50 |
EB16 |
17/02/2014 |
|
|
<20 |
<50 |
<100 |
<50 |
Air Quality
Noise
Water Quality
Land Contamination
Chemical and Waste
Management
Landscape and Visual
Impact
Miscellaneous
5.1.10 No adverse observation was
identified in the reporting period.
Table 5.1 Summary of Environmental
Licensing and Permit Status
Statutory
Reference |
License/
Permit |
License
or Permit No. |
Valid
Period |
Remarks |
|
From |
To |
||||
EIAO |
Environmental Permit |
EP-409/2010 |
10/01/2011 |
N/A |
Yau Tong Bay – Decommissioning of Shipyard
Sites |
WDO |
Chemical Waste Producer Registration |
5213-290-K2822-04 |
22/10/2013 |
N/A |
Whole Construction Site |
WDO |
Billing Account for Disposal of Construction Waste |
7018469 |
N/A |
N/A |
Whole Construction Site |
APCO |
Notification Pursuant to Section 3(1) of
The Air Pollution Control (Construction Dust) Regulation |
365200 |
02/10/2013 |
N/A |
Whole Construction Site |
-
Excavation
of Contaminated Soil in Zones R3, R6, R7, A3, A4, A5, T19A, T22BA, T22BB and
T32C;
-
Formation
of biopiles;
-
Cement
solidification treatment; and
-
Excavation
and disposal of PCBs-Contaminated Soil in Zones T32D and T32E to Landfill.
Air
Quality Impact
·
Nil.
Construction
Noise Impact
·
Nil.
Water
Quality Impact
·
Nil.
Chemical
and Waste Management
·
The nets surrounding retained tress in the site
should be checked to be in proper positions.
Landscape
and Visual Impact
·
Nil.
Miscellaneous
·
Nil.