12
IMPLEMENTATION SCHEDULE OF RECOMMENDED
MITIGATION MEASURES
Table 12.1 Implementation
Schedule for Air Quality Control
EIA Ref # |
Environmental Protection Measures
/ Mitigation Measures |
Location / Timing |
Implementation Agent |
Implementation Stages* |
Relevant Legislation and
Guidelines |
|||
Des |
C |
O |
Dec |
|||||
3.102 3.91 |
Construction
& Demolition Phase Implementation of dust suppression
measures stipulated in Air Pollution Control (Construction Dust) Regulation: ·
skip hoist for material transport should be
totally enclosed by impervious sheeting; ·
every vehicle should be washed to remove any
dusty materials from its body and wheels before leaving a construction site; ·
the area where vehicle washing takes place and
the section of the road between the washing facilities and the exit point
should be paved with concrete, bituminous materials or hardcores; ·
where a site boundary adjoins a road, streets or
other accessible to the public, hording of not less than ·
every stack of more than 20 bags of cement should
be covered entirely by impervious sheeting places in an area sheltered on the
top and the 3 sides; ·
all dusty materials should be sprayed with water
prior to any loading, unloading or transfer operation so as to maintain the
dusty materials wet; ·
the excavation area should be limited to as small
in size as possible and backfilled with clean and/or treated soil shortly
after excavation work; ·
the height from which excavated materials are
dropped should be controlled to a minimum practical height to limit fugitive
dust generation from unloading; ·
the load of dusty materials carried by vehicle
leaving a construction site should be covered entirely by clean impervious
sheeting to ensure dust materials do not leak from the vehicle; and ·
implementation of an environmental monitoring and
auditing program to monitor the construction process in order to enforce
controls and modify method of works if dusty conditions arise. Implementation of precautionary
and mitigation measures for removal of Asbestos Containing Material stipulated
in Air Pollution Control Ordinance: ·
enclosure of the work area; ·
containment and sealing for the asbestos containing
waste; ·
provision of personal decontamination facilities; ·
use of personal decontamination facilities; ·
use of personal respiratory/protection equipment; ·
use of vacuum cleaner fitted with a high
efficiency particulate air filter for cleaning up the works area; and ·
carrying out air quality monitoring during the
asbestos abatement works. |
Works Sites / During Construction Phase |
Contractor |
|
Ö |
|
|
EIAO-TM APCO |
S3.8 – S3.22 and 3.77 3.108 |
Operation Phase ·
Although the final selection of cremation
technology and air pollution control system would be subject to open
tendering procedure, the performance and specifications of the new cremators
and air pollution control system shall fully comply with target emission
limits and the BPM12/2(06); ·
Use of towngas as burning fuel for the new
cremators; and ·
Adoption of flue gas treatment system for joss
paper burners. ·
The monitoring of the air pollutants shall comply
with the requirements of BPM and future Specified Process License of new
crematorium, to be issued by EPD under the APCO. |
Cremators / During Operation Phase |
Contractor |
Ö |
|
Ö Ö |
|
APCO APCO |
# All recommendations and requirements
resulted during the course of EIA/EA Process, including ACE and / or accepted
public comment to the proposed project.
* Des - Design, C - Construction, O –
Operation, and Dec - Decommissioning
Table 12.2 Implementation
Schedule for Waste Management
EIA Ref # |
Environmental Protection Measures/Mitigation
Measures |
Location/ Timing |
Implementation Agent |
Implementation Stages* |
Relevant Legislation and Guidelines |
|||
Des |
C |
O |
Dec |
|||||
S.4.58 |
Construction
& Demolition Phase Good Site Practice ·
Obtain relevant waste disposal permits from the
appropriate authorities, in accordance with the Waste Disposal Ordinance
(Cap. 354), Waste Disposal (Chemical Waste) (General) Regulation (Cap. 354)
and the Land (Miscellaneous Provision) Ordinance (Cap. 28) ·
Prepare a Waste Management Plan approved by the
Engineers / Supervising Officer of the Project based on current best practice
on Construction Site ·
Use waste licensed collector to collect waste ·
Establish trip ticket system as contractual
requirement with reference to ETWB(W) No. 31/2004 for monitoring of public
fill and C&D waste at public filling facilities and landfills. ·
Provide training to site staff in terms of proper
waste management and chemical waste handling procedures ·
Separate chemical wastes for special handling and
dispose them at licensed facility for treatment ·
Provide sufficient waste disposal points and
regular collection for disposal ·
Establish recording system for the amount of
wastes generated, recycled and disposed of |
Project site / design, construction and demolition
phase |
Contractor |
Ö |
Ö |
|
|
Waste Disposal Ordinance
(Cap. 354) Waste Disposal (Chemical
Waste) (General) Regulation Waste Disposal (Charges
for Disposal of Construction Waste) Regulation ETWBTC(W) 19/2005 ETWB(W) No. 31/2004 |
S.4.59 |
Environmental Management
Plan ·
The ETWB TCW No.19/2005 “Environmental Management
on Construction” includes procedures on waste management requiring
contractors to reduce the C&D material to be disposed of during the
course of construction. Under this ETWB TCW No.19/2005, the Contractor is
required to prepare and implement an Environmental Management Plan (EMP) and
the Waste Management Plan (WMP) becomes part of the EMP. |
Project site / design, construction and demolition
phase |
Contractor |
Ö |
Ö |
Ö |
|
ETWBTC(W) 19/2005 |
S.4.60 |
Waste Reduction Measures ·
Prior to disposal of C&D waste, wood, steel
and other metals should be separated for reuse and / or recycling to minimize
the quantity of waste to be disposed of to landfill ·
Minimize use of wood and reuse non-timber
formwork to reduce the amount of C&D waste ·
As far as practicable, segregate and store
different types of waste in different containers, skips or stockpiles to
enhance reuse or recycling of materials and their proper disposal ·
Encourage collection of aluminium cans, plastic
bottles and packaging material (e.g. carton boxes) and office paper |
Project site /
construction and demolition phase |
Contractor |
|
Ö |
Ö |
|
WBCT No. 32/1992 WBCT No. 19/2005 |
S.4.61-S4.62 |
Excavated Materials
Rock and soil generated from excavation should be
reused during site formation and landscaping as far as practicable to reduce
total amount dispose off site.
Trip ticket should be implemented for surplus
excavated materials |
Project site /
construction and demolition phase |
Contractor / ArchSD |
|
Ö |
|
|
WBTC No. 12/2000 ETWB TC(W) No. 31/2004 |
S.4.63 – S.4.66 |
Construction and Demolition Materials
Well-planned
design and good site management can minimize over-loading and generation of
waste materials such as concrete and cement grouts. Wooden frame should be
replaced by metals. Plastic fencing and reusable site office structure can
reduce C&D waste generation.
The
Contractor should recycle as much C&D materials as possible. Proper
segregation of waste types on site to enhance reuse and recycling of
materials. Designated areas for different materials storage should be
assigned for segregation.
Under
the Construction Waste Disposal Charging Scheme, construction waste producers
such as construction and renovation contractors and premises owners, prior
using government waste disposal facilities, need to prepare a billing account
with EPD and pay for construction waste disposal.
It
is expected that trip-ticket system should be implemented for surplus C&D
materials disposal in accordance with ETWB TC(W) No.31/2004 and the
Construction Waste Disposal Charging Scheme. Waste should be delivered to a
public fill reception facility. Copies or counterfoils of trip tickets will
be kept for record purpose. |
Project site /
construction and demolition phase |
Contractor / ArchSD |
Ö |
Ö |
|
|
WBTC No. 2/93 The Land (Miscellaneous
Provision) Ordinance WBTC No. 19/2005 ETWB TC(W) No.31/2004 |
S.4.68 – S.4.70 |
Contaminated Materials –
Further Contamination Investigation
Building
structure of cremators, flues and chimney would likely to be contaminated by
DCM ash due to long term servicing. As the cremators are still in operation,
it is not possible to carry out site investigation in the areas of cremators,
flues and chimney in this stage. To maintain uninterrupted cremation
services, further site investigation in cremation rooms and associated
equipments are proposed to undertake after decommissioning and prior to
demolition of existing crematorium.
According
to the asbestos investigation report, asbestos gasket (woven) and insulation
sheet were identified with ACM. It is also not possible to inspect all potential
asbestos containing material locations due to on-going operation of
cremators, concealed pipeline inside wall and covered up flange connection by
metal cover. Further inspection of the inaccessible locations will be
undertaken prior to demolition works.
Contaminated
ash and ACM potential contamination locations will be further indentified. In
view of close distance between the contaminated ash and ACM, there is concern
on contaminated ash wastes being embedded in ACM. Therefore, it is advisable
to remove contaminated ash waste prior to any asbestos containing material on
building structures. |
Cremators, chimney and flues areas/ After
decommissioning but prior to demolition of the existing crematorium. |
FEHD, ArchSD, Contractor |
|
Ö |
|
|
ProPECC PN 2/97 ProPECC PN 3/94 APCO |
S.4.72 – S 4.73 |
Asbestos Containing Materials
Asbestos
waste will be handled in accordance with the Code of practice on the
Handling, Transportation and Disposal of Asbestos Waste issued by the
Environment and Food Bureau.
Production,
collection and disposal of asbestos waste will follow the “trip-ticket”
system. The registered asbestos contractor will be appointed a licensed
asbestos waste collector to collect the packaged asbestos waste and deliver
to the designated landfill for disposal. Notification has to be given to EPD
for its, Ten working days notice of the intention to dispose of asbestos
waste. After processing the notification, EPD will issue specific
instructions and directions for disposal. |
Cremator room in existing crematorium / before
demolition |
Contractor |
|
Ö |
|
|
COP on Handling,
Transportation and Disposal of Asbestos Waste under the Waste Disposal
(Chemical Waste)(General) Regulation |
S.4.75 |
Demolition, Handling, Treatment and Disposal of Low Contaminated DCM
from Demolition of Existing Crematorium
Where
the ash waste contains low contamination levels of DCM (<1ppb TEQ), the Contractor should avoid ash waste
becoming airborne during demolition. General dust suppression measures will
be followed and ash waste would be directly disposed to landfill. |
Cremator room in existing crematorium / before demolition |
Contractor |
|
Ö |
|
|
ProPECC PN 3/94 APCO |
S.4.76 |
Demolition, Handling, Treatment and
Disposal of Moderately Contaminated DCM from Demolition of Existing
Crematorium
Where the ash waste contains low contamination levels of DCM (>1
and <10 ppb TEQ), the following steps should be followed: ·
Site Preparation - Except the
cremators / flue / chimney, all removable items should be removed as far as
practicable to avoid obstructing the decontamination activities; - Preliminary site
decontamination of all debris should be carried out using High Efficiency
Particulate Air (HEPA) vacuum cleaner; - Top portion of the chimney should be
enclosed by a 3-layer chamber of polyethene sheets; - At the entrance to the cremators/
flues/chimney, a 3-chamber decontamination unit should be constructed for
entry and exit from the work area. The 3-chamber decontamination unit should
comprise a dirty room, a shower room and a clean room of at least 1m x 1m
base with 3-layer of fire retardant polyethylene sheet; - Workers should
carry out decontamination procedure before leaving the work area; - Workers should wear full protective
equipment, nitrile gloves, robber boots and full-face positive pressure
respirator; and - Warning signs in both Chinese
and English should be provided in conspicuous areas. ·
Demolition and Handling - The cremators /
flue / chimney should be removed from top down. Any ash or residues attached
to the cremators / flue / chimney or any other building structure should be
removed by scrubbing and HEPA vacuuming; - Waste generated
from the containment or decontamination unit including the protection
clothing of the workers should be disposed to landfill; and - After removal,
all surfaces should be decontaminated by HEPA vaccum. ·
Treatment and Disposal - Immobilise ash waste by proper mixing
with cement as determined by the pilot mixing and Toxicity Characteristic
Leaching Procedure (TCLP); - Waste material should be placed in polyethylene
lined steel drums for disposal at landfill, the drums should be 16 gauge
steel or thicker and fitted with double bung fixed ends adequately sealed and
well labeled in new or good condition. - Drums should be clearly marked
“DANGEROUS CHEMICAL WASTE” in English and Chinese. Prior agreement of the
disposal criteria must be obtain from EPD and the landfill operator. - As a fall back option, if landfill
disposal criteria cannot be met after immobilization of the ash waste,
disposal at the Chemical Waste Treatment Center (CWTC) should be considered. |
Cremator room in existing crematorium / before demolition |
Contractor |
|
Ö |
|
|
ProPECC PN 3/94 APCO |
S.4.77 |
Demolition, Handling, Treatment and
Disposal of Severely Contaminated DCM from Demolition of Existing Crematorium
Where the ash waste contains severely contamination levels of DCM
(>10ppb TEQ), the following steps should be followed: Site Preparation -
Except the cremators / flue / chimney, all removable items should be removed
as far as practicable to avoid obstructing the decontamination activities; - Preliminary site
decontamination of all debris should be carried out using High Efficiency
Particulate Air (HEPA) vacuum cleaner; - The walls, floor and ceiling of
the cremator room where severely contaminated DCM should be lined with
3-layer chamber of fire retardant polyethene sheets. Top portion of the
chimney above the roof should be enclosed by a 3-layer chamber of polyethene
sheets; - At the entrance to the cremators /
flues / chimney, a 3-chamber decontamination unit should be constructed for
entry and exit from the work area. The 3-chamber decontamination unit should
comprise a dirty room, a shower room and a clean room of at least 1m x 1m
base with 3-layer of fire retardant polyethylene sheet where all workers
would carry out decontamination procedures before leaving the work area; - Air movers should be installed at the
cremator room, and at the bottom of the chimney to exhaust air from work
area. A stand-by air mover should be installed with each of air movers.
Sufficient air movement should be maintained to give a minimum of 6 air
changes per hour to the work area; - New pre-filters and HEPA filters
should be used on the air movers. - Before commencement of the
decommissioning work, a smoke test with non-toxic smoke should be carried out
to confirm the air tightness of the containment; - Workers should wear full protective
equipment, disposable protective coverall (such as Tyvek with shoe covers and
hood), nitrile gloves, rubber boots and full-face positive pressure
respirator equipped with a combination cartridge that filters particulate and
removes organic vapour; and - Warning signs in both Chinese and
English should be provided in conspicuous areas. ·
Decontamination, Demolition and Handling - The cremators /
flue / chimney should be removed from top down. Any ash or residues attached
to the cremators / flue / chimney or any other building structure should be
removed by scrubbing and HEPA vacuuming; - The contaminated
detached sections of the building structure where severely contaminated DCM
is located should be wrapped with 2 layers of fire retardant polyethene
sheets. A third layershould be wrapped and secured with duct tape.
Decontaminate the outer layer of the wrapped flue sections by wet wiping; and - After completion
of removal and decontamination, spary the innermost layer of the fire
retardant polyethene sheet with PVA. Upon drying, peel off and dispose of at
landfill site. ·
Treatment and Disposal - All contaminated ash waste with
severely contaminated DCM removed and the used HEPA filters should be sent to
Chemical Waste Treatment Center (CWTC) at Tsing Yi; and - Other
waste including the building structures and its associated panels as well as
waste generated from this decommissioning works are also considered as
contaminated waste and should be disposed of at designated landfill. Waste
generated from this decommissioning works refer to the polyethene wrapping
sheets should be placed into appropriate containers for disposal. Permit has
to be obtained from the Authority. Disposal trip ticket is required to be
made available as record after disposal. |
Cremator room in existing crematorium / before
demolition |
Contractor |
|
Ö |
|
|
ProPECC PN 3/94 APCO |
S4.78 |
Further investigation
and confirmatory test for ash waste in cremator, chimney and flues should be
carried out on DCM prior to the demolition of the existing crematorium. The
sampling and analysis plan should be prepared and submitted to EPD for
approval. |
Cremators, Chimneys and Flues / before demolition |
Contractor |
|
Ö |
|
|
ProPECC PN 3/94 APCO |
S4.79 |
The mitigation measures stated in Section 4.75
to 4.78 of EIA report aim to address the detailed measures of avoiding cross
contamination of DCM and ACM and should form part of the DCM Assessment Report
which will be submitted to EPD for approval before the commencement of the
demolition of the existing crematorium. |
Cremator room, cremators, chimney and flues
areas/ before demolition |
Contractor |
|
Ö |
|
|
|
S.4.81 – S.4.83 |
Chemical Waste ·
All the chemical waste should be handle
according to the Code of Practice on
the Packaging, Labelling and Storage of Chemical Wastes. The chemical
waste should store and collect by an licensed contractor for disposal at
licensed facility in accordance with the Waste
Disposal (Chemical Waste)(General) Regulation. Containers used for the
storage of chemical waste should be: - Suitable for
substance holding, resistant to corrosion, maintained in good condition and
securely closed; - Capacity of less
than 450 liters unless the specifications have been approved by the EPD; and - Display a label
in English and Chinese in accordance with instructions prescribed in Schedule
2 of the Waste Disposal (Chemical
Waste)(General) Regulation. ·
The storage area for chemical waste should: - Be
clearly labeled and used solely for the storage of chemical waste; - Be enclosed on at least 3 sides; - Have a
impermeable floor and bunding, of capacity to accommodate 110% of the volume
of the largest container or 20% by volume of the chemical waste stored in
that area, whichever is the greatest; - Have adequate ventilation; - Be covered to
prevent rainfall from entering (water collection within the bund must be
tested and disposal as chemical waste if necessary); and - Be properly
arranged so that incompatible materials are adequately separated. ·
The chemical waste should be disposed of by: - A licensed waste
collector; - A facility lisenced to receive
chemical waste, such as CWTC at Tsing Yi, which offers chemical waste
collection service and can supply the necessary storage containers; and - A waste recycling plant as
approved by EPD. |
Project site / demolition |
Contractor |
|
Ö |
|
|
Code of Practice on the
Packaging, Labelling and Storage of Chemical Wastes |
S.4.84 – S.4.85 |
General Refuse ·
General refuse should be stored in enclosed bins or compaction units
separated from C&D and chemical wastes. Waste collector should be
employed by the Contractor to minimize odour, pest and litter impacts. Open
burning of refuse on construction site is prohibited by law. ·
The Contractor should carry out an education programe for workers in
avoiding, reducing, reusing and recycling. This should include provision of
three-colour recycling bins and on site and posters and leaflets advising on
the use of recycling bins. |
Project site / Construction and demolition stage |
Contractor |
|
Ö |
|
|
|
S.4.86- S.4.101 |
Operation Phase ·
Ash and non-combustible residues -The disposal of bone
and non-combustible residues should be properly collected and handled to
avoid dust emissions. In line with the current practices, the bone ash will
be stored in covered containers for collection by the deceased’s relatives
within 2 months upon appointment while the non-combustible residues will be
collected in sealed heavy-duty polyethene bags for disposal at landfill. ·
Chemical Waste - Chemical waste generated from the air pollution system as well
as from machinery maintenance and servicing should be managed in accordance
with the Code of Practice on the
Packaging, Labelling and storage of Chemical Wastes under the provisions
of the Waste Disposal (Chemical
Waste)(General) Regulation. The chemical waste should be collected by
drum-type containers and removed by licensed chemical waste contractor. - Plant / equipment maintenance
schedules should be planned in order to minimize the generation of chemical
waste. - Non-recyclable chemical wastes and
lubricants should be disposed at an appropriate facility, such as EPD
Chemical Waste Treatment Centre at Tsing Yi. Copies or counterfoils from
collection receipts issued by the licensed waste collector should be kept for
record purpose. ·
Fly Ash - Collected and stored in sealed drums provided by the CWTC. - Sealed drums are stored in a designated area and are periodically collected by CWTC (normally two to three weeks interval). - Drums are taken to CWTC where they are incinerated and rendered harmless. - Residues are then disposed of at landfill. ·
General Refuse - Waste
generated in offices should be reduced through segregation and collection of
recyclable waste materials (such as paper). To promote recycling of waste
paper, aluminum cans and plastic bottles, it is recommended to place clearly
labeled recycling bins at designated locations. The recyclable waste
materials should be collected by licensed collectors. - General refuse, other
than segregated recyclable wastes, should be separated from any chemical
waste and stored in coved skips. Food and Environmental Hygiene Department
(FEHD) should remove general refuse from the site on daily basis to minimize
odour, pest and litter impacts. Also open burning of refuse must be strictly
prohibited. |
New crematorium / Operation phase |
FEHD |
|
|
Ö |
|
Code of Practice on
Packaging, Labelling and Storage of Chemical Wastes. Waste Disposal (Chemical
Waste)(General) Regulation |
S.10.5 – S.10.6 |
EM&A ·
To
maintain uninterrupted cremation services, further site investigations are
recommended. Building structures asbestos
investigation and dioxins ash waste investigation are recommended around cremators,
chimney, flues and surrounding areas. |
Cremators, chimney, flues and surrounding areas /
after decommissioning and prior to
demolition |
Contractor |
|
Ö |
|
|
ProPECC PN 2/97 and 3/94 AIR,AMP/AAP to be
sumitted under APCO Further Site
Investigation Plan |
# All recommendations and requirements resulted during
the course of EIA Process, including ACE and / or accepted public comment to
the proposed project.
* Des - Design, C - Construction, O –
Operation, and Dec - Decommissioning
Table 12.3 Implementation
Schedule for Land Contamination
EIA Ref # |
Environmental Protection Measures /
Mitigation Measures |
Location / Timing |
Implementation Agent |
Implementation Stages* |
Relevant Legislation and Guidelines |
|||
Des |
C |
O |
Dec |
|||||
5.29 |
Since
the cremators are still in operation the proposed trial pit location, TP-1,
is possessed by CEDD, it is not possible to carry out site investigation
inside the cremation rooms and at TP-1 at this stage. Further site inspection
of TP-1 and two cremation rooms shall be carried out after decommissioning
and prior to the demolition of the existing crematorium. A supplementary CAP
shall be prepared for EPD endorsement to present detailed sampling and
testing plan for two cremation rooms. Further SI of TP-1 shall be conducted
in accordance with the approved CAP. Findings of site investigation and
appropriate remediation methods shall be presented in supplementary CAR and
RAP for EPD endorsement prior to the commencement of any earthworks. The
extent of contamination, if any, should be estimated based on the depth where
contaminants found, the hydrogeological condition and the contaminants
levels. The actual extent would be determined by confirmatory sampling and
testing. |
Pipeline, Cremator Rooms 1 and 2 / before demolition
of the existing cremators |
Contractor |
|
|
|
√ |
Guidance Note for Contaminated Land Assessment and
Remediation; Guidance Notes for Investigation and Remediation of
Contaminated Sites of: Petrol Filling Stations, Boatyards, and Car Repair /
Dismantling Workshops; Guidance Manual for Use of Risk–Based Remediation
Goals for Contaminated Land Management; and EIAO-TM |
5.40 |
Cement
solidification / stabilization technique is considered as the most practical
and cost-effective method to treat the metals contaminated soil on site. |
Near underground storage tank / During soil
treatment |
Contractor |
|
|
|
√ |
|
5.43 –5.44 |
Confirmatory
soil sampling for closure assessment should be carried out to confirm the
clean-up of the contaminated soil. |
Near underground storage tank / During soil
treatment |
Contractor |
|
|
|
√ |
|
5.46 |
Upon
completion of cement solidification / stabilization, confirmation sampling
and testing shall be undertaken to ensure the cleanup targets have been
attained. |
Near underground storage tank / During soil
treatment |
Contractor |
|
|
|
√ |
|
5.49 |
If
contaminated soil is found underneath the pipeline and at cremator rooms from
the further SI, depending on the contamination extent, possible remediation
methods for organic contaminants could be excavation and biopiling as well as
in-situ soil venting. If the volume of contaminated is found to be small and the
aforesaid remediation methods is infeasible and impracticable, excavation and
landfill disposal could be considered as last resort. Closure assessment in
accordance with Sections 5.43 to 5.44 of EIA Report shall be carried out in
order to confirm the clean-up of contaminated soil. The remediation method
should be determined in the supplementary RAP according to the laboratory
results and estimated quantity of contaminated soil. |
Pipeline, Cremator Rooms 1 and 2 / before demolition
of the existing cremators |
Contractor |
|
|
|
√ |
|
5.50 |
During
removal of the underground storage tank, appropriate precautions should be
taken to avoid contamination. All
fuel tank and associated pipework should be emptied prior to any demolition
work being undertaken. Any
remaining sludge or sediment in the tanks or pipework should be removed and
disposed of as chemical waste in accordance with the appropriate regulation
for disposal of such material. After
removal of the underground storage tank, confirmatory soil sample(s)
underneath the tank should be collected and tested for TPH, VOCs and Pb using
the same approach as mentioned in Sections 5.43 and 5.44 of EIA Report to
ensure that no contamination due to fuel leakage. |
Underground storage tank system / before demolition
of the existing cremators |
Contractor |
|
|
|
√ |
Occupational Safety & Health Ordinance;
Guidelines on Occupational Exposure |
5.57 – 5.58 |
The following basic health and safety measures should be implemented as far as possible: ·
Set
up a list of safety measures for site workers; ·
Provide
written information and training on safety for site workers; ·
Keep
a log-book and plan showing the contaminated zones and clean zones; ·
Maintain
a hygienic working environment; ·
Avoid
dust generation; ·
Provide
face and respiratory protection gear to site workers; ·
Provide
personal protective clothing (e.g. chemical resistant jackboot, liquid tight
gloves) to site workers; and ·
Provide
first aid training and materials to site workers. The Contractor for the excavation works shall take note of the following points for excavation: ·
Excavation
profiles must be properly designed and executed; ·
In
case the soil to be excavated is situated beneath the groundwater table, it
may be necessary to lower the groundwater table by installing well points or
similar means. The discharge of groundwater, if any, should follow the
requirements under the Water Pollution Control Ordinance (WPCO); ·
Excavation
zone should be fenced off; ·
Quantities
of soil to be excavated must be estimated; ·
It
may be necessary to split quantities of soil according to soil type, degree
and nature of contamination; ·
Temporary
storage of soil at intermediate depot or on-site may be required. The storage
site should include protection facilities for leaching into the ground e.g. a
liner may be required; ·
Supply
of suitable clean backfill material is needed after excavation; ·
Care
must be taken of existing buildings and utilities; and ·
Precautions
must be taken to control of ground settlement. · should be disposed of in accordance with the WPCO. |
At contaminated and soil treatment areas/ During
soil treatment |
Contractor |
|
|
|
√ |
Occupational Safety & Health Ordinance;
Guidelines on Occupational Exposure |
5.60 |
The following mitigation measures are recommended to be implemented during CS/S processes. Air
Quality Impact ·
The
loading, unloading, handling, transfer or storage of cement should be carried
out in an enclosed system. ·
The
loading, unloading, handling, transfer or storage of other materials which
may generate airborne dust emissions such as untreated soil and oversize materials
sorted out from the screening plant and stabilized soil stockpiled in the
designated handling area, should be carried out in such a manner to prevent
or minimise dust emissions. These materials should be adequately wetted prior
to and during the loading, unloading and handling operations. ·
All
practicable measures should be taken to prevent or minimize the dust emission
caused by vehicle movement. Noise
Impact ·
The
mixing area should be sited as far as practicable to nearby noise sensitive
receivers. ·
Simultaneous
operation of mixing plants and other equipment should be avoided. ·
Mixing
process and other associated material handling activities should be properly
scheduled to minimise potential cumulative noise impact on nearby noise
sensitive receivers. ·
Construction
Noise Permit should be applied for the operation of powered mechanical
equipment, if any, during restricted hours. Water Quality Impact ·
Stockpile
of untreated soil should be covered as far as practicable to prevent the
contaminated material from leaching out.
The leachate should be discharged following the requirements of Water
Protection Control Ordinance. Waste
·
The
oversize materials such as rocks and boulders should be screened out, cleaned
the soil attached and used as filling material within the site. Contaminated materials (soil or rock
fragments) of size smaller than ·
Stabilized
soils should be broken into suitable size for backfilling or reuse on site. ·
A
high standard of housekeeping should be maintained within the mixing area. ·
There
should be clear and separated areas for stockpiling of untreated and treated
materials. |
At contaminated and soil treatment areas/ During
soil treatment |
Contractor |
|
|
|
√ |
Occupational Safety & Health Ordinance;
Guidelines on Occupational Exposure |
# All recommendations and requirements resulted during
the course of EIA Process, including ACE and / or accepted public comment to
the proposed project.
* Des - Design, C - Construction, O –
Operation, and Dec - Decommissioning
Table 12.4 Implementation
Schedule for Visual Impact
EIA Ref # |
Environmental Protection Measures /
Mitigation Measures |
Location / Timing |
Implementation Agent |
Implementation Stages* |
Relevant Legislation and Guidelines |
|||
Des |
C |
O |
Dec |
|||||
Table 6.4 |
Construction & Demoliton Phase Topsoil, where identified, should
be stripped and stored for re-use in the construction of the soft landscape
works, where practical. |
Work site /
During Construction Phase |
Contractor |
Ö |
Ö |
|
|
EIAO-TM Annex 10, 18 ETWB TCW 2/2004 ETWB
TCW 3/2006 |
Existing trees to be retained on
site should be carefully protected during construction. |
Work site /
During Construction Phase |
Contractor |
Ö |
Ö |
|
|
||
Trees unavoidably affected by the
works should be transplanted where practical. |
Work site /
During Construction Phase |
Contractor |
Ö |
Ö |
|
|
||
Compensatory tree planting should
be provided to compensate for felled trees. |
Work site /
During Construction Phase |
Contractor |
Ö |
Ö |
|
|
||
Control of night-time lighting. |
Work site /
During Construction Phase |
Contractor |
|
Ö |
|
|
||
Erection of decorative screen
hoarding compatible with the surrounding setting. |
Work site /
During Construction Phase |
Contractor |
|
Ö |
|
|
||
Table 6.5 |
Operation Phase Aesthetic design of the
façade/chimneys/noise barriers and associated structures to harmonize with
the surrounding settings. |
Work site /
During Design Stage and Operation Phase |
FEHD |
Ö |
|
Ö |
|
EIAO-TM Annex 10, 18 ETWB TCW 2/2004 ETWB TCW
3/2006 |
Aesthetic design of landscaped
roof. |
Work site /
During Design Stage and Operation Phase |
FEHD |
Ö |
|
Ö |
|
||
Tree and
shrub planting to enhance amenity |
Work site /
During Design Stage and Operation Phase |
FEHD |
Ö |
|
Ö |
|
||
Reinstated of disturbed area. |
Work site /
During Design Stage and Operation Phase |
FEHD |
Ö |
|
Ö |
|
# All recommendations and requirements resulted during
the course of EIA Process, including ACE and / or accepted public comment to
the proposed project.
* Des - Design, C - Construction, O –
Operation, and Dec - Decommissioning
Table 12.5 Implementation
Schedule for Noise Control
EIA Ref # |
Environmental Protection Measures /
Mitigation Measures |
Location / Timing |
Implementation Agent |
Implementation Stages* |
Relevant Legislation and Guidelines |
|||
Des |
C |
O |
Dec |
|||||
S7.49 |
Construction
Phase Use of quiet PME
for excavator/loader, soil nailing drilling
machine, rock dowel drilling machine, bulldozer, dump truck and crawler
mounted rock drill. |
Work site / During construction and demolition phase |
Contractor |
|
Ö |
|
|
EIAO-TM, GW-TM,
NCO |
S7.52 |
Good Site Practice: ·
Only
well-maintained plant should be operated on-site and plant should be serviced
regularly during the construction program; ·
Silencers
or mufflers on construction equipment should be utilized and should be
properly maintained during the construction program; ·
Mobile
plant, if any, should be sited as far from NSRs as possible; ·
Machines
and plant (such as trucks) that may be in intermittent use should be shut
down between work periods or should be throttled down to a minimum; ·
Plant
known to emit noise strongly in one direction should, wherever possible, be
orientated so that the noise is directed away from the nearby NSRs; and ·
Material stockpiles and other structures should be
effectively utilised, wherever practicable, in screening noise from on-site
construction activities. |
Work site / During construction and demolition phase |
Contractor |
|
Ö |
|
|
EIAO-TM, GW-TM,
NCO |
S7.53 |
Operation Phase Provision
of 2.5m high acoustic barriers for a total of 10 radiators. The noise barrier
would be lined with sound absorbing material at the surface of the barrier
facing the noise source. |
Upper roof of the crematorium / During operation
phase |
ArchSD, FEHD |
Ö |
|
Ö |
|
EIAO-TM, NCO |
# All recommendations and requirements resulted during
the course of EIA Process, including ACE and / or accepted public comment to
the proposed project.
* Des - Design, C - Construction, O –
Operation, and Dec - Decommissioning
Table 12.6 Implementation
Schedule for Water Quality Control
EIA Ref # |
Environmental Protection Measures /
Mitigation Measures |
Location / Timing |
Implementation Agent |
Implementation Stages* |
Relevant Legislation and Guidelines |
|||
Des |
C |
O |
Dec |
|||||
S8.30 to S8.52 |
The measures as outlined in the ProPECC PN 1/94 should be followed where applicable. |
Work site / during construction and
demolition phase |
Contractor |
|
Ö |
|
|
Technical
Memorandum on the Environmental Impact Assessment Process (EIAO-TM) Water
Pollution Control Ordinance (WPCO) Technical
Memorandum on Standards for Effluents Discharged into Drainage and Sewerage
Systems, Inland and Coastal Waters (TM-DSS) |
S8.3 and S8.53 |
There is a need to apply to EPD for a discharge licence under the WPCO for discharging effluent from the construction site. The discharge quality is required to meet the requirements specified in the discharge licence. All the runoff, wastewater or extracted groundwater generated from the works areas should be treated as necessary so that it satisfies all the standards listed in the TM-DSS. IMonitoring of the construction site effluent quality should be carried out in accordance with the WPCO license which is under the ambit of regional office (RO) of EPD. |
Work site / during construction and demolition phase |
Contractor |
|
Ö |
|
|
EIAO-TM, WPCO, TM-DSS |
S8.54 |
Temporary sanitary facilities, such as portable chemical toilets, should be employed on-site where necessary to handle sewage from the workforce. A licensed contractor would be responsible for appropriate disposal of waste matter and maintenance of these facilities. |
Work site / during construction and demolition phase |
Contractor |
|
Ö |
|
|
EIAO-TM, WPCO, TM-DSS |
S8.55 |
Good site practices should be adopted to remove rubbish and litter from construction sites so as to prevent the rubbish and litter from spreading from the site area. It is recommended to clean the construction sites on a regular basis. Stockpiles of cement and other construction materials should be kept covered when not being used. |
Work site / during construction and demolition phase |
Contractor |
|
Ö |
|
|
EIAO-TM, WPCO, TM-DSS |
S8.56 |
Oils and fuels should only be used and stored in designated areas which have pollution prevention facilities. To prevent spillage of fuels and solvents to the nearby watercourse, all fuel tanks and storage areas should be provided with locks and be sited on sealed areas, within bunds of a capacity equal to 110% of the storage capacity of the largest tank. The bund should be drained of rainwater after a rain event. Oil leakage or spillage should be contained and cleaned up immediately. |
Work site / during construction and demolition phase |
Contractor |
|
Ö |
|
|
EIAO-TM, WPCO, TM-DSS |
S8.57 |
Handling and disposal of operation stage effluent should follow the practices outlined in ProPECC PN 5/93 where applicable. |
Project site / during design and operation phase |
FEHD |
Ö |
|
Ö |
|
EIAO-TM, WPCO, TM-DSS |
# All recommendations and requirements resulted
during the course of EIA Process, including ACE and / or accepted public
comment to the proposed project.
* Des - Design, C - Construction, O – Operation, and
Dec - Decommissioning