9.1.1
The existing Siu Ho Wan Water
Treatment Works (hereinafter referred to as SHWiu Ho Wan WTW) and the
associated raw water and treated water transfer and distribution systems were
commissioned in 1997 to provide treated water capacity of 150,000 m3/day. It provided treated water to the Hong Kong
International Airport at Chek Lap Kok and the initial phases of North Lantau
New Town and Discovery BayThis sSection investigates the issue of Hazard to Life associated with chlorine, which is used as the major
disinfection agent in theSiu Ho Wan wWater tTreatment wWorks.
9.1.1
With
reference to the Section
3.7 of the EIA Study Brief 3.7, chlorine hazards during construction phase and operation phase will be investigated. For hazards during construction phase, the additional hazards
initiated by construction activities will be
identified by systematic
method (i.e. Hazard and Operability (HAZOP) Study). For operation phase, hazards
associated with chlorine will be assessed if and only if there is an increase
of storage and on-site transport of chlorine.
9.2.1
According to Section 1.2 (i) of the EIA Study Brief, the Project comprises,
inter alias, the extension of Siu Ho Wan WTW from the capacity of 150,000 m3/day to 300,000 m3/day, with an option for
further uprating to 350,000 m3/day. Based on a review update
on the ultimate water demand at this stage, the extension work would only comprise of
uprating to 300,000
m3/day. No further uprating to the capacity of 350,000 m3/day is required for this Project.
9.2.2
For the investigation study under the agreement,
options selection for the appropriate water treatment process has been conducted
by the Consultants. The recommended water treatment process consists of the following:
-
Removal of odour by pre-ozonation;
-
Pre-treatment of manganese by potassium
permanganate;
-
Sedimentation by installation of tube settlers in
clarifiers;
-
Primary disinfection by intermediate ozonation;
-
Filtration by installation of dual media filters
(GAC media and fine sand);
-
Post chlorination for residual chlorine
requirement.
9.2.3
In the original water treatment process, chlorine was proposed for oxidation of impurities
and disinfection. The allowable storage of chlorine in the existing
Siu Ho Wan WTW compound at a capacity of up to 73 tonnes which was endorsed by Co-ordinating Committee
on Land-Use Planning and Control relating to Potentially Hazardous
Installations (CCPHI) on 30.5.1992 during the Stage I WTW, has already duly taken
into account future extension of the WTW up to 300 MLD i.e. 300,000 m3/day.
9.2.4
The recommended water treatment process as endorsed
by WSD in February 2004 adopts "ozone" for primary disinfection with the addition of
potassium permanganate to remove manganese and BAC filter to remove ammonia for the Siu Ho Wan WTW
extension. As such, no chlorine would be required for the
proposed water treatment process under normal condition except for post
chlorination. Chlorine dose would not
exceed the designed dosing capacity of the WTW as defined in the Steering Group Report on
Hazard Assessment, Planning Study and Action Plan endorsed by CCPHI in May 1992. Hence, there
will be no increase of storage and on-site transport of chlorine to that of the
allowable storage capacity for the Siu Ho Wan WTW. With reference to the
Options Selection Report, the chlorine consumption is anticipated to return to
the designed level of the WTW or below. Also, the Final Adoptive Report (dated 15 September 2003) gave a full justification to explain that there would be no increase of chlorine consumption after Siu Ho Wan
WTW is extended. Executive summary of Option Selection Report and relevant
pages of the Final Adoptive Report is attached in Appendix
9.2 and 9.3 respectively. Therefore,
proposed water treatment
process in the extended WTW would induce no increase
of chlorine hazard in terms of storage or number of deliveries. As
a result, the hazard assessment for the operation phase of Siu Ho Wan WTW extension is
not required in the EIA stage and only a HAZOP study was conducted in this EIA Sstudy.
9.3.1
As stipulated in Annex 4 of the Technical Memorandum on Environmental Impact
Assessment Process (EIAO-TM), the societal risk guidelines for acceptable risk
levels has included the ALARP region, which required that risk
within ALARP region should be mitigated to “As Low As Reasonably Practicable”.
In comparing with the “CCPHI Interim
Guideline for Acceptable Societal Risk” (IRG) adopted for the Hazard Assessment, no ALARP region was adopted
for that study. In reviewing the societal risk associated with the water treatment
works assessed in the Hazard Assessment, some of the scenarios, with the
assumptions of implementing several mitigation measures,
would lie
within one to two orders of magnitude below the IRG, which is the ALARP region of the societal risk
guideline stipulated in the TM.
9.3.2
Referring to the recommendations from the Hazard Assessment, it
concluded that any risk within two orders of magnitude of the IRG should be
mitigated as
low as reasonably practical. Also, it
mentioned that
any risk at two orders of magnitude below the IRG may, in ALARP terms, be
considered negligible. Therefore, the Hazard Assessment noted it is unlikely that any
further mitigation measures for the works may be justified and the site may be considered suitable from
the perspective of public safety.
9.3.3 The Hazard Assessment also
concluded that the site selected for the WTW was suitable in terms of the
Interim Risk Guidelines with the implementation of the following risk
mitigation measures:
·
Use reinforced concrete panels in the construction
of the chlorine drum store
·
Adopt “Route 2” (transport liquid chlorine by sea
to Refuse Transfer Station (RTS) near the WTW at Siu Ho Wan and the remaining
short distance to the plant by road) as the primary chlorine transportation
route
·
Restrict the chlorine delivery using the seawall at
or near the RTS at Siu Ho Wan to the weekend or only transport of up to 12
drums by sea to the RTS seawall at any one time with only 26 deliveries per
year
·
Prohibit overnight chlorine drums storage at the
seawall
·
Institute a 30m cordon around the chlorine
unloading point during deliveries and temporary storage within a secure area
surrounded by a steel barrier
9.3.4 The
Hazard Assessment also recommended a 1000 metre radius centred on (excluding land 50m
in altitude above) the Chlorine Building as Consultation Zone for Siu Ho Wan WTW. Moreover, land-use restrictions at Areas 7,
9 and 10 in the Recommended Outline Development Plan (RODP) for the North
Lantau Development were recommended in the Hazard Assessment to ensure the
compliance of Interim Risk Guidelines.
9.3.5 As
confirmed with WSD on the implementation of mitigation measures stated in Section 9.3.3, the
establishment of consultation zone for Siu Ho Wan WTW and the implementation of land-use restrictions in Section 9.3.4 with no change in
land-use for the restricted areas, the societal risk associated with the Siu Ho Wan WTW
would have
been no change from that previously assessed in the Hazard Assessment.
9.4.1
The HAZOP Study was carried out in several stages:
·
Define the scope of the Study
·
Select the HAZOP Study Team
·
Prepare for the HAZOP Study MeetingHAZOP
·
Execute HAZOP Study Meeting
·
Report the Study Results
Define the scope of the Study
9.4.2
The scope of the Study is in line with the EIA Study Brief, which is:
i)
Identify additional hazards initiated by
construction activities which may increase the risk of chlorine accidents
during storage, handling, transport
ii)
Recommend risk mitigation measures for
implementation during construction phase
Select the HAZOP Study Team
9.4.3
The team members were selected in a manner that could ensure the Study Tteam would have sufficient knowledge of the following items:
a)
Design of the existing and future extended Siu Ho Wan WTW
b)
Daily operation of the existing Siu Ho Wan WTW
c)
Maintenance and repair works at existing Siu Ho Wan WTW
d)
Chemical properties of chemicals/compounds involved
in operation and extension work of Siu Ho Wan WTW
e)
Safety issues encountered at the existing Siu Ho Wan WTW and future extension
works
f)
Environmental issues encountered in future Siu Ho
Wan WTW extension works
Collect necessary dataPrepare for the HAZOP Study Meeting
9.4.4
Prior to the HAZOP Study meeting, the following
information were gatheredThe preparation work prior to the HAZOP Study
Meeting involved:
Collect
useful information
Information collected prior to the Study Meeting included the followings:
·
Locations of the chlorine storage area and chlorine
pipework
·
Chlorine delivery procedures and travel route of Cchlorine Ddelivery
Ttruck on site
·
Chlorine handling and emergency procedures
·
ExpectedPossible construction activities and corresponding plants/equipment involved in the extension works
·
Material Safety Data Sheet (MSDS) of chemicals and
material encountered/to
be encountered during the Wwater
Ttreatment Wworks
operation and extension construction worksactivities
Convert the
collected
information into a suitable form
In order to provide concise and easy-understanding information to the Study Team
members, the
collected information were converted into layout plan and summary table.
Plan the Study Meeting
sequence
Prior to the sStudy
mMeeting,
a
Study Meeting sequence was prepared to ensure the Study Meeting could proceed smoothly and
systematically. During the preparative work, it
was planned that the
Study Meeting would
be conducted in a construction activity-based
sequence. That is, all the expectedpossible extension construction
activities and plants/equipment involved would be discussed in turn to identify possible
hazards and mitigation measures.
Arrange Study Meeting
After necessary information was obtained and Study
Meeting sequence was planned, all the Study Team members were invited to attend
the Study Meeting. In the meantime, obtained information (in form of layout plan and summary
table) and Study
Meeting sequence were sent to the Study Team members for their
preparation before the meeting.
Execute HAZOP Study Meeting
One HAZOP Study Meeting session was carried out on 5 February 2004. Representatives from WSD, M&E and MEMCL
participated in the Study Meeting. The items discussed were recorded during the
Study Meeting.
Report the
Study Results
Key findings in the Study including causes of the hazard imitatinginitiating events and the corresponding
mitigation measures are presented in the following Sectionsparagraphs.
9.5.1
The Siu Ho Wan Water Treatment Works is located in Area 4 on the Siu Ho Wan
Layout Plan No.L/I-SHW/1Tai Ho Wan Area 4, with area about 5.8ha. For the HAZOP Study,
locations of chlorine-related facilities and travel
route of chlorine delivery truck in the
existing Siu Ho Wan WTW compound are of interest.
A layout plan showing locations of Chlorine
Building, chlorine piepeworks and chlorine delivery truck
travel route is given in Figure 9.1.
9.5.2
Description of the Project has been given in Section
2. As agreed in the HAZOP Study Meeting, only construction
activities inside the Siu Ho Wan WTW compound were discussed in the HAZOP Study because construction works outside the Siu Ho Wan WTW compound were considered unlikely to initiate additional hazards related to chlorine. The construction activities and corresponding plants/equipment discussed in the Study Meeting were listed in Table 9.1.
Table 9.1 Construction Activities and Corresponding Plants/equipment Discussed
in HAZOP Study Meeting
Extension Work Component |
Construction Activity Group |
Construction Activity |
Plant |
A. General Site Activities |
A1. Site
clearance and site formation |
1.
Excavation 2. Removing debris |
1. Backhoe 2. Bulldozer 3. Dump truck |
A2. Access
road
construction |
1.
Excavation 2.
Removing debris 3.
Paving road |
1. Backhoe 2. Dump truck |
|
A3. Electricity
generation and supply |
1. Generate electricity 2. Preparing electricity supply
facilities and connecting electricity transmission wire |
1. Generator |
|
A4. Site
personnel, plants and equipment mobilization |
1. Mobilizing personnel, equipment and plants
by vehicles and crane |
1. Site vehicle 2. Crane lorry 3. Mobile crane |
|
A5. Material/Waste
storage |
1. Storing/stockpiling of material/waste
2. Material/waste delivery |
1. Truck 2. Crane lorry |
|
A6. Operations related to fire |
1. Cooking
by on-site personnel 2. Welding |
1. Welding machines 2. Catering equipment 3. Liquid/gas fuel |
|
A7. Chemicals/fuel storage |
1. Chemicals/fuel
storage 2. Transporting chemicals/fuel |
1. Chemicals/fuel
delivery vehicle 2. Crane lorry |
|
B. Stage
II Extension – Construction of Laboratory Extension |
B1.
Temporary works for temporary earth retaining structure, bulk excavation,
piling and foundation work |
1. Excavation 2. Piling works 3. Concrete slab demolition 4. Transporting large objects and equipment |
1.
Backhoe 2.
Oscillator 3.
Pneumatic
breaker 4.
Roller 5.
Air
compressor 6.
Tower
crane 7.
Dump truck |
B2.
Form work erection and rebar refixing |
1.
Fixing
steel 2.
Mobilization of pile of steel
by crane 3.
Welding |
1.
Welding
machine 2.
Mobile
crane 3.
Tower
crane |
|
B. Stage II Extension – Construction of Laboratory Extension |
B3. Concreting |
1.
Mixing
concrete 2.
Pour
concrete into structure |
1.
Concrete mixer 2.
Crane
lorry 3.
Tower Crane 4.
Backhoe 5.
Vibrator
|
B4. Column
and Roof |
1. Transferring large objects and equipment |
1. Mobile crane |
|
B5. Brickwork and finishing |
1. Welding 2. Transferring large objects and equipment |
1.
Backhoe 2.
Mobile crane 3.
Welding
machine |
|
B6. E&M installation |
1. Welding 2. Transferring large objects and equipment |
1.
Mobile
crane
2.
Backhoe 3.
Welding
machine |
|
B7. Landscaping Work |
1. Excavation for soft landscape works implementation 2. Tree plantation for soft landscape works |
1.
Backhoe 2.
Crane
lorry |
|
C. Stage
II Extension- Construction of Sludge Thickener and Washwater Tank |
C1.
Temporary works for temporary earth retaining structure, bulk excavation,
piling and foundation work |
1. Excavation 2. Piling
works 3. Concrete
slab demolition 4. Transporting
large objects and
equipment |
1.
Backhoe 2.
Oscillator 3.
Pneumatic breaker 4.
Roller 5.
Air compressor 6.
Tower crane 7.
Dump truck |
C2.
Form work erection and rebar refixing |
1.
Fixing steel 2.
Mobilization of pile of steel
by crane 3.
Welding |
1.
Welding machine 2.
Mobile crane 3.
Tower crane |
|
C3. Concreting |
1.
Mixing concrete 2.
Pour concrete into structure |
1.
Concrete
mixer 2.
Crane lorry 3.
Tower Crane 4.
Backhoe 5.
Vibrator |
|
C4. Column and Roof |
1. Transferring
large objects and equipment |
1. Mobile crane |
|
C. Stage II Extension- Construction Sludge Thickener and Washwater Tank |
C5. Brickwork and finishing |
1. Welding 2. Transferring
large objects and equipment |
1.
Backhoe 2.
Mobile
crane 3.
Welding machine |
C6. E&M installation |
1. Welding
2. Transferring
large objects and equipment |
1.
Mobile crane 2.
Backhoe 3.
Welding machine |
|
C7. Landscaping Work |
1. Excavation
for soft landscape works implementation 2. Tree
plantation for soft landscape works |
1.
Backhoe 2.
Crane lorry |
|
D. Stage
II Extension – Construction of Pre-treatment Contact Chambers, Rapid Mix
Chambers, Flocculation Tanks, Sedimentation Basins, Intermediate Ozone Tank
and BAC Filters |
D1. Temporary works for temporary
earth retaining structure, bulk excavation, piling and foundation work |
1. Excavation 2. Piling
works 3. Transporting
large objects and equipment |
1.
Backhoe 2.
Oscillator 3.
Pneumatic breaker 4.
Roller 5.
Air compressor 6.
Tower crane |
D2.
Form work erection and rebar refixing |
1.
Fixing steel 2.
Mobilization of pile of steel
by crane 3.
Welding |
1.
Welding machine 2.
Mobile crane 3.
Tower crane |
|
D3. Concreting |
1.
Mixing concrete 2.
Pour concrete into structure |
1.
Concrete
mixer 2.
Crane lorry 3.
Tower Crane 4.
Backhoe 5.
Vibrator |
|
D4. Column and Roof |
1. Transferring large objects and equipment |
1. Mobile crane |
|
D5. Brickwork and finishing |
1. Welding 2. Transferring
large objects and equipment |
1.
Backhoe 2.
Mobile
crane 3.
Welding machine |
|
D6. E&M installation |
1. Welding
2. Transferring
large objects and equipment |
1.
Mobile crane 2.
Backhoe 3.
Welding machine |
|
D. Stage II Extension – Construction of
Pre-treatment Contact Chambers, Rapid Mix Chambers, Flocculation Tanks,
Sedimentation Basins, Intermediate Ozone Tank and BAC Filters |
D7. Landscaping Work |
1. Excavation
for soft landscape works implementation 2. Tree
plantation for soft landscape works |
1.
Backhoe 2.
Crane lorry |
E. Stage II Extension – Construction of Lime Saturators |
E1. Temporary
works for temporary earth retaining structure, bulk excavation, piling and
foundation work |
1. Excavation 2. Concrete
slab demolition 3. Transporting
large objects and equipment |
1.
Backhoe 2.
Oscillator 3.
Pneumatic breaker 4.
Roller 5.
Air compressor 6.
Tower crane 7.
Dump truck |
E2.
Form work erection and rebar refixing |
1.
Fixing steel 2.
Mobilization of pile of steel
by crane 3.
Welding |
1.
Welding machine 2.
Mobile crane |
|
E3. Concreting |
1.
Mixing concrete 2.
Pour concrete into structure |
1.
Concrete
mixer 2.
Crane lorry 3.
Backhoe 4.
Vibrator |
|
E4. Brickwork and finishing |
1. Welding 2. Transferring
large objects and equipment |
1.
Backhoe 2.
Mobile
crane 3.
Welding machine |
|
E5. E&M installation |
1. Welding
2. Transferring
large objects and equipment |
1.
Mobile crane 2.
Backhoe 3.
Welding machine |
|
E6. Landscaping Work |
1. Excavation
for soft landscape works implementation 2. Tree
plantation for soft landscape works |
1.
Backhoe 2.
Crane lorry |
|
F. Stage II Extension – Installation of one additional Filter Press |
F1. E&M installation |
1. Welding
2. Transferring
large objects and equipment |
1.
Mobile crane 2.
Backhoe 3.
Welding machine |
G. Stage II Extension-
Construction of
Ozonation Building/ Facilities
|
G1. Form
work erection and rebar refixing |
1.
Fixing steel 2.
Mobilization of pile of steel
by crane 3.
Welding |
1.
Welding machine 2.
Mobile crane 3.
Tower crane |
G2. Concreting |
1. Mixing
concrete 2. Pour
concrete into structure |
1.
Concrete
mixer 2.
Crane lorry 3.
Backhoe 4.
Vibrator |
|
G3. Column and roof |
1. Transferring large objects and equipment |
1. Mobile crane |
|
G4. Brickwork and finishing |
1. Welding 2. Transferring
large objects and equipment |
1.
Backhoe 2.
Mobile
crane 3.
Welding machine |
|
G5. E&M installation |
1. Welding
2. Transferring
large objects and equipment |
1.
Mobile crane 2.
Backhoe 3.
Welding machine |
|
G6. Landscaping work |
1. Excavation
for soft landscape works implementation 2. Tree
plantation for soft landscape works |
1.
Backhoe 2.
Crane lorry |
|
H. Stage II Extension – Construction of Pipeline Extension |
H1. Pipeline laying |
1. Excavation 2. Transferring
pipeline 3. Connecting
extended pipework 4. Welding |
1.
Backhoe 2.
Crane lorry 3. Welding machine |
I. Stage II Extension – Testing and
Commissioning of Chlorine-related Extension Installation |
I1. Testing and Commissioning |
1. Check
the reliability of the equipment 2. Purge
the gaseous nitrogen through the extended pipework 3. Inject
chlorinated water into the contact tank |
|
J. Stage II Extension – Testing and Commissioning of
Ozone-related Installation |
J1. Testing and Commissioning |
1. Check
the reliability of the equipment 2. Purge
the gaseous nitrogen through the extended pipework 3. Inject
ozone into the contact tank |
|
K. Stage I Modification – Installation of Pumps for Siu Ho Wan Raw
Water and Fresh Water Pumping Station |
K1. E&M installation |
1. Retrofitting water pump with higher capacity, including
installation of additional pumps and replacement of existing pumps |
1.
Crane lorry 2.
Welding machine |
L. Stage I Modification – Converting one Sedimentation Basin into
an Intermediate Ozone Contact Tank |
L1. Demolition work |
1. Demolition
of concrete slab of existing facilities 2. Removing
debris |
1.
Pneumatic breaker 2.
Dump truck |
L2. Retrofitting
works and E&M works |
1. Transferring
large objects and equipment 2. Retrofitting
the ozone contact tank equipment 3. Welding |
1.
Crane lorry 2.
Backhoe 3.
Welding machine |
|
M. Stage I Modification –
Retrofitting of Lamella Settlers in the Sedimentation Basins |
M1. Demolition Work |
1. Demolition
of concrete slab of existing facilities 2. Removing
debris |
1.
Pneumatic breaker 2.
Dump truck |
M2. E&M installation |
1.
Retrofitting
lamella settlers 2.
Welding |
1.
Crane lorry 2.
Tower crane 3.
Welding machine |
|
N. Stage I Modification – Installation of Equipment for Alum Sludge Holding Tanks Nos.
3 & 4 inside
Chemical Storage Building |
N1. E&M installation |
1. Provision
of equipment for alum sludge holding tanks 2. Welding |
1.
Crane lorry 2.
Welding machine |
Introduction
9.6.1
A HAZOP Study is the method for identifying hazards
and problems which prevent efficient operation. It is a technique whichthat provides
opportunities for people to let their imaginations go free and think of all
possible ways in which hazards or operationg problem might arise.
Moreover, it is done in a systematic way in order to reduce the chance that something is missed,. which dDuring the Study, each component of the Project (construction activity and corresponding plants/equipment in this case) and each sort of hazard is
considered in turn. The Study is conducted by a team so that the
team members can stimulate each other and build upon ideas from each other.
9.1.1Water Supplies Department (WSD) commissioned consultants to conducted a
Preliminary Project Feasibility Study (hereinafter
referred to PPFS) in respect of the project “Siu Ho Wan Water Treatment Works
Extension” (hereinafter referred to as the Project) in January
1999. The PPFS summarized the
requirements of the Project and described the studies undertaken and the new
works required, together with the outline designs for principal elements of the
Project, cost estimate, land requirements and implementation programme.
9.1.1Following the PPFS, Metcalf
& Eddy Ltd. has been commissioned by WSD to carry out the Extension of Siu
Ho Wan Water Treatment Works Investigation (the Project) under
Agreement No. CE 75/2002 (WS) (the Assignment).
9.1.1
The
objective of this Assignment is to investigate into the feasibility of the
proposed extension of SHW WTW. The
Assignment is as follows:
·To
produce the optimum preliminary design and to define the outline of the works
to enable detailed design to proceed;
·To
identify all technical requirements/constraints including operational land,
environmental impact, hydraulic, surge and geotechnical, etc. and to establish
the acceptability and practicability of the works;
·To
identify the site conditions and factors that have to be considered in the
detailed design;
·To
carry out an Environmental Impact Assessment (EIA) study and to obtain
Environmental Permit for the Project; and
·To
prepare contract strategy, programme and cost estimates for the works.
9.1.1The commencement date of
the Assignment is 10 June 2003 and the study period is scheduled to be 18
months.
The
locations of the Project Works are shown in Figures 1.1a and 1.1b. The layout plan of SHW WTW Extension is
illustrated in Figure 1.2. The
Project will comprise the following:
(a) Extension of the Siu Ho
Wan Water Treatment Works from the capacity of 150,000 m3/day
to 300,000 m3/day together with the
associated uprating of the capacity
of the Siu Ho Wan Raw Water and Fresh Water Pumping Stations;
(b) Construction of the
proposed Siu Ho Wan Raw Booster Pumping Station and laying of the associated
water mains;
(c)Demolition and
reprovision of the existing Pui O Pumping Station;
(c)Uprate of capacity of
the Pui O No. 2 Raw Water Pumping Station; and
(c)Duplication of two
sections, approximately 2km, of 1200mm diameter water mains at Pui O.
9.1.1In accordance with the Project Study Brief, an initial assessment of the
environmental impacts arising from the Project is required to identify those
environmental issues of key concern during the construction and operation phases of the Project
that require more detailed assessment.
The findings of the initial
assessment are presented in this Initial Assessment Report (IAR).
9.1.1The Project is a designated
project under Schedule 2, Part I(E2) of the Environmental Impact
Assessment Ordinance (EIAO) (Cap. 499) and requires an environmental permit
under the EIAO for the implementation of the Project. The Project Profile (No. PP-073/2000) for the
Project was submitted to EPD on 17 January 2000. The EIA Study Brief (No. ESB-046/2000) for an Environmental
Impact Assessment (EIA) study brief under
section 5(7)(a) of the EIAO was issued by the EPD on 15 February 2000.
9.1.1The purposemain objective of the EIA
Study is to provide information on the nature and extent of environmental
impacts arising from the construction and operation of the proposed Project and
related activities taking place concurrently.
The information will contribute to decisions on:
·overall acceptability of any
adverse environmental consequences that are likely to arise as a result of the
proposed Project;
·the conditions and requirements
for the detailed design, construction and operation of the proposed Project to
mitigate against adverse environmental consequences wherever practicable; and
·the acceptability of residual impacts after the
proposed mitigation measures are implemented.
the acceptability of
residual impacts after the proposed mitigation measures are implemented.
9.1.1This IAR will provide
an initial assessment of the potential environmental impacts in relation to the
following likely key issues associated with the Project. e
objectives of the EIA Study are as follows:
(a)to
describe the proposed Project and associated works together with the
requirements for carrying out the proposed Project;
(a)to identify
and describe the elements of the community and environment likely to be
affected by the proposed Project and/or likely to cause adverse impacts to the
proposed Project, including both the natural and man-made environment;
(a)to identify
and quantify emission sources and determine the significance of impacts on
sensitive receivers and potential affected uses;
(a)to
identify and quantify any potential losses or damage to flora, fauna and
natural habitats;
(a)to
identify any negative impacts on sites of cultural heritage and to propose
measures to mitigate these impacts;
(a)to identify any
potential landscape and visual impacts and to propose measures to mitigate
these impacts;
(a)to propose the provision
of infrastruture or mitigation measures so as to minimize pollution,
environmental disturbance and nuisance during construction and operation of the
project;
(a)to identify, predict and
evaluate the residual (i.e. after practicable mitigation) environmental impacts
and the cumulative effects expected to arise during the construction and
operation phases of the project
in relation to the sensitive receivers and potential affected uses;
(a)to identify, assesses and
specify methods, measures and standards, to be included in the detailed design,
construction and operation of the project
which are necessary to mitigate these environmental impacts and reducing them
to acceptable levels;
(a)to investigate the
extent of side-effects of proposed mitigation measures that may lead to other
forms of impacts;
(a)to identify constraints
associated with the mitigation measures recommended in the EIA study; and
to design and specify
the environmental monitoring and audit requirements, if required, to ensure the
implementation and the effectiveness of the environmental protection and
pollution and pollution control measures adopted.
9.1.1The Assessment Area for the purpose of the EIA Study,
as specified in the BriefEIA Study Brief, is
presented below:
·Air quality assessment – the assessment area shall
be a distance of 500m from the Project boundary.
·Noise impact assessment – include all areas within
300 m from the Project boundary. If the
first layer of noise sensitive receivers provides acoustic shielding to those
receivers further from the site, the assessment area could be reduced
accordingly, subject to the agreement of DEP.
·Water quality impact assessment - the assessment area for the water quality impact
assessment is defined by a distance of 500m from the Project site
boundary. include
all areas within 500 m from the Project boundary. The area shall include but not limited to Pui O freshwater stream.
·Ecological impact assessment - the assessment area
for terrestrial ecological assessment shall include all areas within 500 m
distance from the site boundary of the works areas, or the area likely to be
impacted by the Project. For aquatic
ecology, the assessment area shall be the same as for water quality assessment.
·Landscape and visual impacts - the assessment area
for landscape impact assessment shall include all areas within a 500 m distance
from the work limit of the proposed Project, while the assessment area for the
visual impact assessment shall be defined by the visual envelope of the
Project.
·Cultural heritage impact study - all sites of
cultural heritage that might be adversely affected by the impacts due to
construction activities of the Project.
·Hazard
assessment – consultation
zone for hazard assessment of the Potentially Hazardous Installation at SHW WTW as
shown in Figure 9.1.
9.1.1The remainder of the report is organised as
follows:
i)understanding
of EIA Study objectives and key environmental issues;
i)proposed
approach and methodology;
i)programme
for the EIA Study; and
·environmental
study teamSection 2 - Project Description & Option Evaluation
·Section 3 – Air Quality Impact
·Section 4 – Noise Impact
·Section 5 – Water Quality Impact
·Section 6 - Ecological Impact
·Section 7 – Landscape and Visual Impact
·Section 8 - Cultural Heritage Impact
·Section 9 - Hazard to
Life
·Section 10 - Waste Management Implications
·Section 11 - Environmental Monitoring
& Audit
·Section 12 – Overall Conclusions
CVs of
key study team members are presented in Appendix A.
UNDERSTANDING
of OBJECTIVES & key issuesproject
description
Understanding of
ObjectivesIntroduction
The site for the proposed Siu Ho Wan Treatment
Works extension is within the boundary of the existing Siu Ho Wan Treatment
Works. The location of the site is
about 100m south of the North Lantau Highway which is bounded by a Sewage
Treatment Plant in the southwest and North Lantau Service Road in the north. The proposed
location is illustrated in Figure 2.1a
The site for the
proposed raw water booster pumping station is located immediately next to the entrance of Siu Ho
Wan shown in Figure 2.1a. The proposed site
will have an area of approximately 0.5 hectares and the pumping statin will be
about 8m in height. One of the
alternative sites is proposed to located 800m South from Ta Pang Po
The proposed site of the Project is located on the The locations of the Project Works are shown in
Figures 1.1a and 1.1b. The layout plan
of SHW WTW Extension is illustrated in Figure 1.2. The Project comprises the following:
(a) Extension
of the Siu Ho Wan Water Treatment Works from the capacity of 150,000 m3/day
to 300,000 m3/day together with the associated uprating of the fresh
water pumping capacity of the Siu Ho Wan Raw Water and Fresh Water Pumping
Station;
(b) Construction
of the proposed Siu Ho Wan Raw Water Booster Pumping Station and laying of the
associated water mains;
Demolition and reprovision of the existing Pui O
Raw Water Pumping Station;
Uprate of capacity of the Pui O No. 2 Raw Water
Pumping Station; and
Duplication of two sections, approximately 2km, of
1200mm diameter water mains at Pui O.
The SHW WTW extension
Project is a Designated Project under Schedule 2, Part I(E) of the EIA
Ordinance. One of the main objectives
of the Assignment is to undertake an EIA Study to fulfil the statutory
requirements of the Ordinance, and to assist WSD to obtain the Environmental
Permit for this Project.
Figures 2.1, 2.2 and
2.3 illustrate the key environmental issues in relation to the Project.
Noise ImpactConstruction
and Operational Activities
Construction noise generated from
powered mechanical equipment(PME) for activities such as site clearance,
earthworks and concreting would be an issue given the proximity of noise
sensitive receivers (NSR) in close vicinity to the works at Pui O such as
village houses of Lo Uk Tsuen, Pui O San Wan, Pui O Lo Wan, BPui O Public
School and Pui O Rural Committee Office.
The potential operational noise sources
would be arising from the pumps of the proposed pumping stations. Houses at the Pui O Lo Wan close to the Pui
O pumping stations would require control of operational noise.
Ecological ImpactsNeed of the
Project
The Project Profile indicated
that woodland/shrubland habitat loss of about 8000 m2 for
alternative alignment and 1600 m2 for the option
of laying most of the pipeline under the existing road at Pui O.
In addition, the key ecological
resources that may be impacted included the followings:
Woodland habitat of
Lantau South Country Park – cut across by a short section of the alternative
alignment near the northern end
Pui O wetlands – directly
impacted by alternative alignment
Natural streams and Pui O
mangrove stand
Cultural HeritageConsideration
of Alternative Options
The Pui O No. 2 Raw Water Pumping
Station and associated water mains falls within the known Pui O Archaeological
Site. Findings to date indicate that the site was occupied or used during the
historic period. Burials belonging to
the Six (A.D. 220-589) and Qing Dynasties (A.D. 1644-1911) have been excavated
at Pui O. These findings are relatively unique in the Territory. Kiln structures and related features dated
to the Tang Dynasty (A.D. 618-907) have also been recorded. Although the site has not yielded
prehistoric findings, its landform and location suggests such deposits may be
present.
Works at Pui O are in proximity
to historical buildings and other features associated with the villages of Pui
O Lo Wai Tsuen and Pui O San Wai Tsuen.
Landscape & Visual
Given that the proposed WTW
extension and Raw Water Booster Pumping Station would be in a
developed area of the Siu Ho Wan area with an established “industrial”
character, potential landscape and visual impacts would be low. The proposed booster pumping station may create
visual and landscape impact along the North Lantau Highway (NLH) which is the
gateway corridor of Hong Kong. The
key pPotential
impacts of the Project would also be expected mainly
in the Pui O area.
Construction of the Pui O Raw Water Pumping Station and main laying
would have visual impact, given the proximity to visually sensitive receivers
particularly residents next to the existing pumping station or any nearby
historical buildings. Main landscape
impact would be loss of vegetated areas particularly woodlands (e.g.
in the Lantau South CP).
Water Quality
Potential sources of impact on
water quality during the construction works would include:
Construction runoff and drainage.
General construction activities
e.g. debris, refuse and liquid spillage of any fuels stored on-site.
Sewage effluents from the
construction workforce.
Disturbance to or loss of aquatic
systems.
Impacts on Water Sensitive
Receivers such as Siu Ho Wan, Pui O Beach, stream courses and mangroves would
require proper site management practices.
The water pollution control measures would be required to prevent the
construction works affecting the treatment process at the SHW WTW.
Waste Management
Good management and disposal of
excavated material and construction waste will be required. Sludge and wastewater would be the main
operational waste and should be strictly managed and disposedal of.
Construction activities of the Project may initiate
additional risk of chlorine accidents during transport, handling and storage of
chlorine in the existing WTW.
In the operational phase of the Project, if there
is an increase of storage and on-site transport of chlorine, the associated risk
would be higher than that evaluated previously in the Hazard Assessment Study
conducted in 1992 and its compliance with the Risk Guidelines would need to be evaluated.
Air
Quality
Potential dust impacts may be
arising from Cc on the nearby air sensitive receivers, especially the Pui O village houses. The
implementation of the dust
suppression measures would be required.
may initiate additional risk of chlorine
accidents during transport, handling and storage of chlorine in the existing
WTW.
APPROACH AND METHODOLOGYAir Quality
The technical approach
to undertake the EIA Study
for the environmental issues outlined in Section 2 is presented below. All
impact assessments will be carried out in accordance with the requirements of
the EIAO Technical Memorandum
(TM) and the EIA Study Brief. The EIA Study will take into account of the
potential cumulative impacts with any major concurrent projects in the
vicinity.
Inception
StageEnvironmental Legislation and Standards
Task 1: Study
Initiation, Data Collection and
Review
The latest relevant background
information and reports on the study area from AMO, EPD, DSD, AFCD and PlanD,
will be obtained. The data and study
reports will be collated and to
provide an updated baseline profile of existing conditions.
Baseline
StageBaseline Conditions
Task 2: Baseline
Review
The review of relevant
reports and studies will be continued to establish in detail the baseline
environmental profile of the assessment area.
Field visits will be undertaken to confirm and update the nature of the
study area and surroundings, and the baseline data and sensitive receivers.
Task 3: Field Survey and
Investigation
Field surveys or
investigations will be initiated to fill in the data gaps identified in the
baseline review and to complete the environmental baseline profile of the
assessment area.
Task 4: Alternatives
Options Input
Based on the literature
review and interim data available from the project specific field surveys and
investigations, an initial review of potential environmental impacts of
alternative options will be undertaken and input provided to the evaluation of
alternative siting or alignment options.
Detailed
Assessment StageAir Sensitive Receivers
Detailed assessment of
environmental issues will be undertaken based on the preferred siting, design
and alignment option.
Assessment Methodology & Criteria
Task 5: Ecological
Impact
A review of the
ecological data will be undertaken including HKU Biodiversity Survey and Hong
Kong Breeding Bird Survey and recent surveys on Pui O area from relevant
studies.
More specific ecological
surveys will be undertaken to fill in the identified data gaps and update the
previous data, in liaison with AFCD.
Ecological Surveys
The field surveys will
focus on the proposed works areas, and be undertaken for a duration of at least
3 months, covering the wet season. The surveys will cover habitats, vegetation,
birds, mammals, aquatic communities, herpetofauna and invertebrates (butterfly
& dragonfly).
The surveys will focus
on the work areas, and also covering the area 500m from the works area.
Impact Assessment
A habitat map will be
produced, showing sites of conservation importance, as well as distribution and
abundance of any rare or protected species within the assessment area. The
establishment of baseline ecological conditions and impact assessment will
follow the EIAO TM requirements and
criteria (Annexes 8 and 16), evaluating both on‑site and off‑site
impacts quantitatively where possible.
Ecological impacts to be addressed include the direct, indirect and
cumulative impacts of habitat loss, and disturbance associated with
construction and operation of the Project, with particular attention to the
impact on conservation areas. Practical mitigation measures will be
recommended, to avoid, minimize, and/or compensate for the adverse ecological
impacts identified and ensure there is no unacceptable impact.
Task 6: Cultural
Heritage
A desk-based study will
be undertaken to compile all available information regarding the cultural
heritage potential within close proximity to the study corridor.
If the desk-based study
identifies any additional areas of archaeological potential within the Study
Area the Antiquities and Monuments Office may require a field
investigation to be carried out to verify this potential.Historical
buildings and structures as well as other resources, which fall within the AMO
definition as presented in the Criteria
for Cultural Heritage Impact Assessment will be recorded
through a comprehensive field survey. The scope of the survey has been defined
in the brief. All identified
cultural heritage features will be recorded using standardised recording
forms.The historical value of and potential impacts on the identified
structures and any identified archaeological deposits will be evaluated
following accepted standards and procedures. Measures will be recommended to
mitigate the impacts of the proposed works.
The findings of the desk-based study, the
built heritage and archaeology
survey, if required, and the assessment and mitigation recommendations;
including plans, master layout plan and cross-referenced check-list would be
presented in the report.
Task
7: Landscape and Visual Impact
The methodology will
follow the Brief requirements, section 1 of Annex 10 and Annex 18 of the Technical
Memorandum of the EIA
Ordinance (EIAO-TM) and related Explanatory Notes.
A baseline desktop study
of relevant plans and studies, and site inspection of the area will produce and
map an inventory of the key landscape and visual features of the assessment
area. The baseline study will also
identify the representative viewpoints or visually sensitive receivers.
The impact assessment
will examine the construction and operational impact of the Project on the
existing landscape and identified visually sensitive receivers within the
visual envelope. The landscape impact
will be quantified in terms of the approximate area loss of main landscape
features such as woodland area. The level and significance of the landscape and
visual impact will be based on an established system with criteria such as
number of receivers and duration of impact.
Mitigation measures will
be proposed to minimise potential impacts and the proposed mitigation measures
will be illustrated graphically, such as by photomontages.
Task
8: Water Quality Impact
The water system(s) and sensitive receivers which
may be affected during the construction and operation stages of the Project
will be identified and confirmed through a site visit. All the identified
sources of potential water quality impact will be evaluated and their impact
significance determined, such as impacts due to construction runoff and
drainage, sediment resuspension from excavation works and downstream siltation
impacts, and water pollution due to site construction activities.
Requirements for
mitigation measures to minimize any identified adverse impacts on the water
system(s) and sensitive receivers will be recommended. The use of containment structures and
diversion channels is recommended wherever practicable to facilitate a dry or
at least confined excavation within watercourses. By limiting or confining the works areas the extent of
disturbance to the surrounding wetland habitats will be significantly reduced,
and thus resulting impacts on water quality from sediment resuspension will be
reduced.
Task 9: Noise Impact
Potential noise impacts
will be assessed in accordance with the criteria and methodology given in the
TM made under the Noise Control Ordinance, EIAO, and also the Hong Kong
Planning Standards and Guidelines. Construction works associated with this
Project would elevate ambient noise levels in areas immediately adjacent to
excavation zones and along the access route used to transport construction
materials and equipment and to export excavated spoil material. Construction
noise impact will be assessed. Sound power levels from the potential
construction equipment plants will be established and the noise impacts on the
identified noise sensitive receivers (NSRs) will be calculated. Appropriate noise mitigation measures such
as quietened equipment, noise barriers, will be recommended. During operation
phase, noise from proposed plant and equipment such as pumps, will be
controlled, where necessary, by careful location of plant, or acoustic
shielding/cover.
Task 10: Waste
Management
Waste generation sources
(e.g. excavated land-based materials, general construction wastes, chemical
wastes and sludge from WTW) will be identified, quantified and characterized.
Appropriate waste handling, on-site storage (chemical wastes & sludge),
transportation and disposal routes for each type of waste will be recommended.
The assessment and recommendation will be undertaken with reference to the
requirements in Waste Control Ordinance, its subsequent legislation and regulations.
Task 11: Construction
Air Quality Impact
An emission inventory
will be developed and construction dust impact of the proposed engineering
works on Air Sensitive Receivers (ASR) will be assessed.
Task 12: Hazard to Life
A Hazard and Operability
(HAZOP) study will be conducted to identify additional hazards initiated by
construction activities. The HAZOP
study will cover the possible failure events, human errors and external hazards
initiated by the construction activities (e.g. excavation) which may increase
the risk of chlorine accidents during storage, handling and transport of
chlorine. Risk mitigation measures to
be implemented during construction phase will be proposed where necessary.
A quantitative risk
assessment (QRA) Study will be conducted if (and only if) there is an increase
of storage and on-site transport of chlorine in the operational phase of the
Project. Relevant information such as data on engineering designs and
operational practices, information of subject site area, existing / future
population data, meteorological data and other necessary data will collected at
the initial stage of the QRA Study.
Potential hazards and estimating associated frequencies by reviewing
design of the water treatment works system and by making reference to relevant
local and international studies will be identified.
Task 13: Preparation of
ReportsIdentification of Environmental Impacts
Construction Phase
The findings,
conclusions and recommendations of the detailed assessment will be assimilated
and presented in a Final EIA Report (including an
Executive Summary and EM&A Manual) for submission to EPD under the EIAO for
formal approval. The recommended
mitigation measures and EM&A requirements for the construction and operational
phases of the Project will be presented in the Final EIA
Report, together with the Implementation Schedule.
Operational Phase
Construction Phase
Operational Phase
In order to assess and evaluate the air quality
impact arising from the proposed Project, detail assessment will be carried out in the subsequent Draft
Environmental Impact Assessment Stage.
STUDY programme
A preliminary study
programme for the Assignment is presented in Figure 4.1. This illustrates the sequence of the various
tasks to be undertaken over the duration of the EIA Study as detailed in
Section 3.
Deliverable and Meeting
Schedule
A tentative schedule of
the deliverable submission dates is presented in Table 4.1.
Table 4.1 Key
Deliverables Submission
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Team Members
9.1.1The
HAZOP Study Team members consisted of 16 members:
Anna Chung Team
leader, MEMCL
C.F. Lai Engineer
(Project Management), WSD
W.K. Yeung Chemist, WSD
L.H. Li Senior
Chemist, WSD
P.W. Lee Engineer, WSD
K.K. Wong Mechanical Engineer (Maintenance), WSD
W.K. Lui Mechanical
Engineer (Project), WSD
K.Y. Tse Electrical Engineer (Project), WSD
F.C. Cheung Electrical
Engineer (Maintenance), WSD
L.M. Chan Engineer
(Design), WSD
K.S. Kong Senior
Engineer (Safety), WSD
K.C. Cheung Assistant
Inspector, WSD
C.W. Lee Senior
Inspector, WSD
Angela Wong Project
Engineer, M&E
Arthur Lee Safety
Representative, MEMCL
Wilson Kwok Environmental
Representative, MEMCL
Methodology
9.6.2
The basic concept of this HAZOP Study, is to take full description of the expected construction activities by a summary table
(as shown in Table 9.1) and an extension layout plan (as shown in Figure 9.1), then to question every construction activity and its corresponding plants/equipment to
discover what deviation[1] from the intention[2] of the activities can occur and what their causes[3] and consequences[4] would be. This is executed systematically by applying
suitable guidewords, which can assist prompt thinking about what might go
wrong.
9.6.3
In the Study Meeting, all construction activities (and corresponding plants/equipment) arewere discussed in turn with the procedures explainedlisted as follows:
1. Explain the
intention of the
construction activity (and corresponding
plants/equipment) to be discussed
2. Identify
possible deviations of the construction activity (and corresponding plants/equipment) being
discussed. The possible deviations were detected by
systematic application of guidewords
3. Spot possible causes of the identified deviations
4. Evaluate the possible consequences due to
the deviation identified
5. Recommend possible mitigation measures
to avoid the occurrence of the deviations
6. Identify the
responsible parties to implement the recommended mitigation measures
7. Record the
findings and recommendation during the discussion
HAZOP Study Execution
9.6.4
One session of the Study Meeting was conducted. The Study Meeting was conducted in the following sequence:
1. Clarified the scope and objectives of this HAZOP Study, which were stated in the EIA Study Brief to the Study Team
2. Explained the
definition of ‘hazard’ to be identified, methodology and procedure of the HAZOP Study to the Study Team
3. Presented each
process of the proposed extension works of Siu Ho Wan WTW to the Study Team
4. Finalized the possible construction
activities (and corresponding plants/equipment) to be discussed in the Study
5. Discussed each
possible construction activity in turn with procedure listed in Section 9.4.3.
6. The Study Meeting ended after all
possible construction activity were discussed
9.7.1
As mentioned in Section 9.4.4, the followings were
identified or
recommended during
the HAZOP Study:
·
Causes of possible deviations
·
Hazardous scenarios which could lead to chlorine leakage/release (i.e. consequence)
·
Mitigation measures to avoid occurrence of
deviations and
corresponding responsible parties
9.7.2
The aim of the HAZOP Study is to identify additional chlorine
hazards during construction additional hazards and mitigate them as far as possible. It is considered that each of the identified
hazardous scenarios could cause personnel injury or fatality including WSD
staff and construction workers on site.
In order to mitigate the possible hazards
identified, all the mitigation measures identified by the HAZOP team and
suggested by FSD are to be incorporated in the construction contract to ensure
their implementation.
9.7.3
As suggested by EPD, a summary description of interface between construction activity and the Chlorine Building is given in Table 9.2. It should
be noted that most of the activities presented in the Table below could cause hazard to the Chlorine Building if
they are operated at an inappropriate location (i.e. too close to the Chlorine
Building). Ensuring the activities to be implemented at
appropriate location would be an effective mitigation measures.
Table 9.2 Interface between Construction Activities and the Chlorine Building
Construction
Activity/ Plant |
Interface |
Excavation near Chlorine Building |
Too much excavation may
|
Piling
Works |
Too much vibration may lead to structural damage of Chlorine
Building |
Demolition
of concrete slab of existing facilities by pneumatic breaker |
Inappropriate method
of demolition may cause damage to chlorine dosing pipework, which causes chlorine leakage. |
Backhoe Bulldozer Dump
truck Site
Vehicle Crane
lorry Mobile
crane Roller Tower
Crane |
Construction
plant/equipment |
Preparing
electricity supply facilities and connecting electricity transmission wire in Chlorine Building |
Accidents initiated by electricity supply
facilities installed inside/adjacent to Chlorine Building could cause damage to the chlorine-related
installation |
Generator, air compressor |
Fire/explosion of generator may cause structural
damage to the Chlorine Building |
Mobilizing
personnel |
Construction workers enter Chlorine Building
without supervision; may cause damage to chlorine-related facilities |
Mobilizing
construction equipment/ plant |
Construction equipment/ plant being mobilized
causes impact on Chlorine Building; may cause structural damage to Chlorine
Building |
Storing/stockpiling
of material/waste near Chlorine Building |
Fire accidents involving stored flammable waste
near Chlorine Building impose fire hazard to Chlorine Building |
Cooking
by on-site personnel near Chlorine Building |
Accidents involving fuels used in cooking causes
fire hazard to Chlorine Building |
Welding
near Chlorine Building |
Accidents involving fuels used in welding and
sparks produced during the operation cause fire hazard to Chlorine Building |
Chemicals/fuel
storage near Chlorine Building |
Fire of chemicals/fuel stored may impose fire
hazard to the Chlorine Building |
Transferring
pile of steel/
large objects and equipment |
Inappropriate transferring operation could |
Tree
plantation for soft landscape works |
Roots of planted trees (with unknown extent of
roots) near Chlorine Building may cause structural |
9.7.4
The above items identified during the HAZOP Study
were summarized into
different categories in Tables 9.32 –
9.45 as shown below. Appendix 9.1 summarized
the mitigation measures to be incorporated in the construction contract.
Table 9.32 Summary
of Identified Possible Deviation Causes
Category |
Identified Possible Deviation Causes |
Lack of monitoring and investigation |
·
Lack
of monitoring of the construction activities ·
Lack
of investigation on the consequence of construction activities to chlorine-related facilities |
Poor chemicals/waste/material management and storage |
·
Accumulation
of stacked debris ·
Too much material stockpiled ·
Too
much chemicals/fuel stored ·
Chemicals/waste/material
stored at inappropriate locations ·
Fire
accidents involving
flammable waste/fuels/chemicals |
Poor maintenance
or installation of plant/equipment |
·
Poor
maintenance of equipment ·
Damage
of equipment undetected ·
Malfunction
of brake of vehicles ·
Insecure
plant/equipment installation
(e.g. counter weight of tower crane) |
Inappropriate location of construction activity |
·
Construction
activity on travelling route of Chlorine Delivery Truck ·
Construction
activity too close to Chlorine Building ·
Construction
activity too close to ·
Excavation
takes place at locations
which underground chlorine pipeworks are installed |
Inappropriate equipment operation |
·
Operator
unable to properly manipulate the equipment ·
Equipment
overloaded ·
Speed
of vehicle is too high |
Conflict to chlorine delivery operation |
·
Equipment/vehicle
is idle or working near/along the Chlorine Delivery Truck traveling route ·
The
chlorine delivery operation and chemicals/fuel delivery operation are
conducted on site simultaneously |
Miscellaneous |
·
Too
high vibration intensity caused by piling works ·
Construction
workers are not aware about the locations accommodating chlorine-related
facilities ·
Plantation
of trees with unknown extent of roots ·
Extended
chlorine pipework connection |
Table 9.43 Summary of Hazardous Scenarios could leading to Chlorine Leakage/release
Identified Hazardous Scenarios |
·
Structural damage to Chlorine
Building ·
Damage to chlorine dosing
facilities ·
Damage to Chlorine pipeworks ·
Obstruct Chlorine Delivery
Truck access route; could cause accident of the
vehicle ·
Cause Chlorine Delivery Truck
unsuitable for driving;
could cause accident of the vehicle ·
Vehicle/equipment crashes to
Chlorine Delivery Truck, or vice versa ·
Fire hazard to chlorine related-facilities |
Table 9.54 Summary
of Mitigation Measures to Avoid Occurrence
of Deviations and Corresponding
Responsible Parties
Category |
Mitigation
Measures Identified |
Parties
Responsible |
Monitoring
and Inspection |
·
Monitor the excavation
activity to avoid excavation to the wrong depth (too much excavation) ·
Conduct monitoring to ensure
the stability of building during construction phase ·
Inspection and supervision to
ensure operation of equipment properly ·
Inspection of excavation
progress near Chlorine
Building and Chemical
Storage Building |
·
Contractor ·
Contractor ·
Safety Officer (Contractor)/ Contractor ·
Safety Officer (Contractor)/ Contractor |
Management |
Waste Management ·
Ensure good C&D waste
management ·
Provide on-site sorting of
debris to avoid excessive debris accumulation ·
Provide temporary storage for
debris at appropriate location ·
Ensure flammable waste is stored at
appropriate/designated location Traffic Management ·
Maintain access roads as a
freeway ·
Provide sufficient
maintenance of the vehicle/generator/equipment ·
Set a speed limit for site
vehicle ·
Propose a designated route
for site vehicles, avoid site vehicle using travelling route of the Chlorine
Delivery Truck ·
Provide adequate fire
fighting equipment at the storage area ·
Provide clear road signs for
site vehicles ·
Install hump on the access
roads to reduce the speed of site vehicles ·
Provide crash barrier to
protect the ·
No parking on access road, or
proper parking area designated for dump trucks Chemicals/material Management ·
Ensure good management of
material delivery to avoid excessive material stock on site ·
Avoid incompatible chemicals
storing together; provide separate storage locations for different chemicals
which are incompatible to each other ·
Provide appropriate labels
according to Dangerous Goods Ordinance ·
Follow Fire Services
Department’s requirement for flammable waste storage ·
Keep the amount of flammable
waste stored in a minimum level ·
Ensure adequate separation
distance between each flammable material storage area ·
No stockpile of material near
the Chlorine Building and the access road is allowed Construction Activity/personnel Management Personnel ·
Ensure sufficient guarding at
Siu Ho Wan WTW to provide sufficient access control ·
Provide clear indication of
rooms accommodating chlorine-related facilities and their hazards
Activity ·
Propose a communication
system between operator of Siu Ho Wan WTW and the Contractor on the date of chlorine delivery to the WTW ·
Prepare a safety ·
Propose a “Permit-to-move”
system for large equipment/plant movement: ·
Contractor provides WSD a
list indicating the number and type of equipment/plant to be mobilized,
equipment/plant movement route and mobilization methodology ·
A risk assessment is
conducted by Safety Officer (Contractor) ·
No equipment/plant movement
should be allowed before approval from WSD/Safety Officer is obtained ·
The “Permit” shall restrict
the time period that equipment/plant can be mobilized ·
Supervision of permitted work
by Safety Representatives from Contractor ·
Follow WSD’s “Permit-to-work”
System for extended chlorine pipework connection ·
No connection work can
commence before approval from WSD is obtained ·
Supervision of permitted works by the
Contractor’s Safety Representative ·
No blasting operation on site
is allowed ·
Define restricted zone for
the equipment (i.e. keep the equipment from the Chlorine Building at a safe ·
Restrict excavation along
travelling route of the Chlorine
Delivery Truck ·
Limit the reach of the tower
crane used ·
Ensure generators are placed
at a safe distance from Chlorine
Building ·
Provide indication/sign for
chlorine pipeworks ·
Provide method statement with
protective measures for the chlorine
dosing pipeworks (and other facilities) ·
Avoid welding operation
inside buildings installed with chlorine pipeworks ·
If welding is unavoidable,
“Hot-work permit” system should be applied for welding operation inside buildings installed
with chlorine pipeworks: ·
No welding work is allowed
before approval from WSD is obtained ·
Provide supervision to the
operations inside buildings installed with chlorine pipeworks by the Safety
Representative from Contractor Landscaping Work Management ·
Avoid plantation of deep root
trees near buildings, especially Chlorine Building |
·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
WSD/ Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
WSD/ Contractor ·
WSD/ Contractor
·
WSD/ Contractor ·
Contractor ·
WSD/ Safety Officer (Contractor)/
Contractor ·
WSD/ Safety Representative (Contractor)/ Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
Contractor ·
WSD/ Safety Representative
(Contractor)/ Contractor
·
Contractor |
Investigation |
·
Investigate the lateral
support of buildings/excavation to ensure proposed extent of
excavation would not affect building stability ·
Locate chlorine pipeworks
before execute excavation |
·
Engineer/ Contractor ·
Contractor |
Training
|
·
Provide adequate training to
equipment operator; implement a license system that only competent persons
could operate the equipment ·
Provide adequate training to
construction workers on the rooms accommodating chlorine-related facilities
and their associated hazards · Provide adequate training to construction workers
on the nature and hazards of chlorine, safety precautions and emergency
measures for leakage of chlorine from drums, piping or installations. |
·
Contractor ·
Contractor · Contractor |
Other Recommendations
9.7.5
The Study Team identified a number of measures during the meeting, which are not
directly associated with additional chlorine hazard discussed above. However, they are considered as appropriate measures to be implemented
during the construction stage. These measures are presented as
follows:
i) To maintain all access roads of fire engine/FSD
vehicles/ambulance as a freeway because Fire Services/Rescue personnel may
approach the location of chlorine leakage from different directions, which depends
on the wind direction. No
equipment/plants and site vehicle is allowed to
park on the access roads. The Contractor
should take the responsibility to implement this mitigation measure.
ii) Some emissions could initiate chlorine leak/smoke
detector alarm (i.e. cause false alarm), which severely affects the operation
of the Water Treatment Works, those emissions are listed as follows:
·
Dust from site clearance and excavation work
·
Smoke from welding work
·
Fuel vapour from electricity generation
·
Exhaust gas from construction equipment and
vehicles
·
Chemicals such as bitumen, paints, organic solvent
etc.
Contractor
should implement mitigation measures to avoid occurrence of false alarm by the
following mitigation measures:
·
Provide dust suppression measures such as covering
the dusty material
·
Implement “Hot-work Permit” system and provide
sufficient ventilation during welding operation to avoid accumulation of smoke
·
Place the generators away from the chlorine
leak/smoke detector alarms
·
Park the construction equipment and vehicles away
from the Chlorine Building
·
Notify WSD prior to the use of chemical compounds and provide
sufficient ventilation during operation involving chemicals
iii) An emergency plan should be proposed to ensure appropriate and quick
response of site staff to evacuate safely in case of chlorine leakage events,
the emergency plan shallould include the following
items/objectives:
·
Provide a system for logging in-out record of all
site staff, which could assist immediate investigation and rescue in a chlorine
leak incident when required
·
Ensure construction workers be familiar with
chlorine alarm system (e.g. proper training)
·
Propose construction workers to participate regular
joint chlorine leak drill with arranged by WSD, and inform local fire
stations in advance.
·
Propose alternative assembly point(s) for
construction workers in case of chlorine leakage event
The measures above shallould be included in the Safety Plan
and emergency plan
for the extension of Siu Ho Wan
WTWconstruction
project. It
would be the responsibility of the Contractor for the safety plan and emergency plan preparation. Copies of the safety and
emergency plans shouldshall be provided to local
fire stations for information. During the
construction stage, the Contractor and staff of SHW WTW shouldshall brief local fire
stations for the implementation of safety and emergency plans.
9.7.6
Further to this draft EIA report, aA number of recommendations were suggested by FSD, which are not
directly associated with additional chlorine hazard but which are also also of same importanceconsidered appropriate to be implemented during
the construction stage. These measures
are presented as follows:
i)
For the storage, conveyance and use of Ppotassium permanganate, Nnitrogen and other substances giving inflammable vapour during the construction
stage, the Contractor should follow the requirements stipulated in Dangerous
Goods Ordinance and its subsidiary regulations
ii)
For the storage and conveyance of chemical waste,
the Contractor should follow EPD’s requirement
iii)
Any vegetation near the cChlorine bBuilding or work site should be trimmed to prevent the spread of fire
iv)
Sufficient number of fire extinguishers should be
provided .
9.1.1A
HAZOP Study was conducted to identify additional chlorine hazards initiated by constructions activities and recommend corresponding mitigation measures
for implementation in construction
stage. The Study was conducted by a Study Team consisted of representatives from WSD, M&E and MEMCL.
9.1.1During
the HAZOP Study, all possible construction activity and corresponding
plants/equipment were discussed in turn.
Causes of possible
deviations, hazardous scenarios and
corresponding mitigation measures were identified or recommended in the Study.
9.1.1Moreover,
a number of measures which are
not directly associated with additional chlorine hazards were identified during
the Study. These measures were considered as appropriate measures to be
implemented during the construction stage and were included in this EIA Report.
9.1.1As
it is expected that the proposed water treatment process after the Water
Treatment Works extension works would induce no increase of chlorine hazard in
terms of storage or
number of deliveries, the hazard assessment for
the operational phase is not required in this EIA Study
Study Team Organisation
Metcalf & Eddy will
be leading the Assignment with technical support from specialists. Figure 5.1
shows the Study Team organisation chart.
Experiences and
qualifications of key study team members of the EIA Study are outlined below
and more fully described in the CVs in Appendix A.
Project
Direction and Management
Project Director – K L Wong is
Managing Director of M&E’s Hong Kong office who has more than 43 years of
water and civil engineering experience.
He retired as Director of Water Supplies after 32 years service in WSD
and is very familiar with the local supply systems and treatment works planning
and design, especially the Shek Pik Reservoir, Tai Lam Chung Reservoir and
Plover Cove Scheme. He has gained extensive experience in the design and
construction of major water supply facilities including water treatment works,
pumping stations, service reservoirs and water mains during his service in WSD
and is also fully conversant with the day-to-day operation and maintenance of
the WSD supply and distribution systems.
He is a water supply specialist and has on many occasions provided
expertise advice on matters pertaining to treatment works, pumping stations,
water mains and service reservoir design.
In his recent years of consultancy practice, he has been Project
Director for many WSD projects, the more relevant ones being Investigation
Study for In-situ Reprovisioning of Sha Tin WTW, Transfer Facilities in
Butterfly Valley, Extension of Water Supply to Ma On Shan and Shau Kei Wan, and
Replacement and Rehabilitation of Watermains Stage 1 Phase 1B Package 1 and
Package 3 (D&C).
Project Manager –
Bevis Mak is an Executive Director of M&E.
He has over 20 years practical experience in the planning,
investigation, design and administration of multi-disciplinary water supply,
environmental and sewage disposal projects, including the design of the Au Tau
Water Treatment Works Stage I and II, the Waterworks Sludge Treatment and
Transfer Facilities. Other major
projects included Pak Kong Water Treatment Works and Transfer Facilities, water
quality studies on the effect of cryptosporidium and giardia in drinking water,
effect of chloral hydrate in drinking water, feasibility of re-using grey water
and treated effluent from secondary sewage treatment works, pressure management
and its effect on leakage control, and Rehabilitation and Replacement of
Watermains. On the sewage and drainage
side, he was responsible for the design and construction of the Sham Tseng
Sewage Treatment Works, East Kowloon Sewage Stage II, North West Kowloon Sewage
Stage II & III (Phase 1), Tolo Sewage Stage I Phase II. He is also a specialist in construction contract
law and was the consultant’s in house contract adviser on the HATS (previously
SSDS) major tunnellng dispute between Government and the Contractor.
Deputy
Project Manager - Michael Leung is an Associate of M&E with 20 years of
experience in water supply and other environmental engineering projects in Hong
Kong and Australia. Michael has
extensive experience in managing projects for feasibility studies, design and
tender documentation involving water treatment works, pumping stations,
watermains and service reservoirs construction in Hong Kong, China and
Australia. He was project manager for investigation projects of WSD mainlaying
in Replacement and Rehabilitation of Watermains Stage 1 Phase 1B Package 3,
Water Transfer Facilities in Butterfly Valley (using H2ONET for network
analysis), and Tsuen Wan/Kwai Chung. Currently, he is project manager for
Replacement and Rehabilitation of Watermains Stage 1 Ph 1B Package 1 and Water
Supply to N-W Tuen Mun. He has in depth
knowledge of the operation of WSD’s water supply systems.
Environmental Team
Environmental Team
Leader – Josh Lam, an Associate of MEMCL, with extensive experience in
environmental management, planning and impact assessment. He is also an ecology and tree survey
specialist. He has been managing and directing numerous multi-disciplinary
environmental projects, ecological and conservation studies: Reconstruction of
Catchwater and Upgrading of Slopes on Hong Kong Island and Lantau, Route10,
Penny’s Bay Infrastructure Development, NENT Planning and Development,
Northshore Lantau and International Theme Park Developments, San Tin Main
Drainage Channel Improvements, Yuen Long/Kam Tin Sewage Disposal.
Hazard Assessment –
Matthew Ko is an Associate with MEMCL, has 11 years of environmental research
and consulting. He has managed over numerous risk assessment projects for
private and public clients, including the recent work for the Towngas Western
Harbour Submarine Pipeline and Associated Station project. He was the Environmental Team Leader for the
EIA for Lai Ping Road, Shatin, Ngau Tam Mei Water Treatment Works, EIA for Kai
Tak Airport North Apron Decommissioning, and Yau Tong Bay Reclamation.
Environmental Impact Assessment –
Jane Carbray is a Senior Environmental Consultant of MEMCL has over 9 years
experience in EIA studies relating to water quality and waste management
issues. She provided specialist inputs to projects such as San Tin EMDC,
Penny’s Bay Infrastructure Development, Tai O Development, NNT Drainage
Masterplan Study, Restoration of Shuen Wan and Urban Landfills, Wanchai
Development Phase II, Feasibility
Study for Intensification and Extension of Tseung Kwan O New Town, Yau Tong Bay Development
and EPD Cumulative Impact Study and Strategic Sewage
Disposal Scheme (SSDS) EIA. She has been also
engaged in waterworks projects including environmental review for the PPFS of
Extension of North Point Supply System, Replacement and Rehabilitation of Water
Mains in Kowloon and NT South.
Air Quality & Noise Assessment –
Anna Chung is a Senior Environmental Consultant of MEMCL has over 6 years
experience in EIA studies major relating to air quality and noise issues. She
provided specialist inputs to projects such as Hong Kong Cyber Port Project
Development, South East Kowloon Development Feasibility Study, Tai O
Development, Wanchai Development Phase II, D&C of Central – Wanchai Bypass
and IECL, Sai Kung Sewage Treatment Works Phase II Upgrading, Outlying Islands
Sewerage Stage 1 Phase II Package J – Sok Kwu Wan Sewage Collection, Treatment
& Disposal Facilities, and Feasibility Study for Intensification and Extension
of Tseung Kwan O New Town.
Ecological/Tree
Specialist - Dr. David Gallacher, an Environmental Consultant
of MEMCL who is an experienced ecologist with academic and practical experience
in many aspects of terrestrial and aquatic ecology. Dr.
Gallacher has extensive experience in tree survey, ecological review and impact
assessment for terrestrial and stream habitats, flora and fauna. Relevant recent projects include: Route 9,
Route 10, Decommissioning of Cheoy Lee Shipyard, Landslide Mitigation Works
Against Natural Terrain Hazards in Tung Wan and Shatin Heights, Construction of
Tuen Mun North No. 2 Fresh Water Service Reservoir and Associated Mainlaying,
Reconstruction of Catchwater Channels and Tunnels and Upgrading of Adjoining
Slopes in Tai Lam Chung, Stage 1, Replacement and Rehabilitation of Water Mains
in Hong Kong and Lantau Island.
Archaeologist/Cultural Heritage Impact Specialist –
Dr Pamela Rogers, is a
Consultant to MEMCL and is a qualified archaeologist and cultural heritage
manager with more than 25 years experience mostly on the heritage of Hong
Kong. She has successfully completed a
wide range of projects for both government and corporate clients, including assessments
of New Territories drainage improvement schemes and several project sites in
Lantau, such as Lantau N-S Road Link Study and Northshore Lantau Development
Feasibility Study. Dr. Rogers is a
member of the Town Planning Board and is active in organisations promoting
heritage management in Hong Kong.
Landscape & Visual Specialist - Salina Lee, is
Landscape Architect of MEMCL and is a Registered Landscape Architect in Hong
Kong with over 7 years of local experience.
She has extensive experience in impact assessment, tree survey and felling
application, landscape masterplan, detailing and planting design, slope
treatment, contract specification, tendering and administration, implementation
of hard and soft landscaping works, site supervision, as well as architectural
surface finish design, for a wide range of projects such as North Lantau
Highway and Tiu Keng Leng Site Formation Works.