EIA Ref. |
EM&A Log Ref |
Recommended Mitigation Measures (What Measures) |
Objectives of the recommended Measures &
Main Concerns to address (What Requirements) |
Who to implement the measures? (Who) |
Location of the measures (Where) |
When to Implement the measures? (When) |
Implementation Status |
||||||||||
Construction
Dust Impact |
|||||||||||||||||
S3.8 |
D1 |
Mitigation measures in
form of regular watering under a good site practice should be adopted.
Watering once per hour on exposed worksites and haul road is proposed to
achieve dust removal efficiency of 92.1%. While the above watering
frequencies are to be followed, the extent of watering may vary depending on
actual site conditions but should be sufficient to maintain an equivalent
intensity of no less than 1.7 L/m2 to achieve the respective dust removal
efficiencies |
Minimize
dust impact at the nearby sensitive receivers |
Contractor |
All
construction sites |
Construction phase |
* |
||||||||||
S3.8 |
D2 |
The Contractor shall
follow the procedures and requirements given in the Air Pollution Control
(Construction Dust) Regulation. |
Minimize
dust impact at the nearby sensitive receivers |
Contractor |
All
construction sites |
Construction phase |
* |
||||||||||
S3.8 |
D3 |
Following dust
suppression measures should also be incorporated by the Contractor to control
the dust nuisance throughout the construction Phase •
Any excavated or
stockpile of dusty material should be covered entirely by impervious sheeting
or sprayed with water to maintain the entire surface wet and then removed or
backfilled or reinstated where practicable within 24 hours of the excavation
or unloading; •
Any dusty materials
remaining after a stockpile is removed should be wetted with water and
cleared from the surface of roads; •
A stockpile of dusty
material should not be extend beyond the pedestrian barriers, fencing or
traffic cones; •
The load of dusty
materials on a vehicle leaving a construction site should be covered entirely
by impervious sheeting to ensure that the dusty materials do not leak from
the vehicle; •
Where practicable,
vehicle washing facilities with high pressure water jet should be provided at
every discernible or designated vehicle exit point. The area where vehicle
washing takes place and the road section between the washing facilities and
the exit point should be paved with concrete, bituminous materials or
hardcores; •
When there are open
excavation and reinstatement works, hoarding of not less than 2.4m high
should be provided as far as practicable along the site boundary with
provision for public crossing. Good site practice shall also be adopted by
the Contractor to ensure the conditions of the hoardings are properly
maintained throughout the construction period. •
The portion of any road
leading only to construction site that is within 30m of a vehicle entrance or
exit should be kept clear of dusty materials; •
Surfaces where any
pneumatic or power-driven drilling, cutting, polishing or other mechanical
breaking operation takes place should be sprayed with water or a dust suppression
chemical continuously; •
Any area that involves
demolition activities should be sprayed with water or a dust suppression
chemical immediately prior to, during and immediately after the activities so
as to maintain the entire surface wet; •
Where a scaffolding is
erected around the perimeter of a building under construction, effective dust
screens, sheeting or netting should be provided to enclose the scaffolding
from the ground floor level of the building, or a canopy should be provided
from the first floor level up to the highest level of the scaffolding; •
Any skip hoist for
material transport should be totally enclosed by impervious sheeting; •
Every stock of more than
20 bags of cement or dry pulverised fuel ash (PFA) should be covered entirely
by impervious sheeting or placed in an area sheltered on the top and the 3
sides; •
Cement or dry PFA
delivered in bulk should be stored in a closed silo fitted with an audible
high level alarm which is interlocked with the material filling line and no
overfilling is allowed; •
Loading, unloading,
transfer, handling or storage of bulk cement or dry PFA should be carried out
in a totally enclosed system or facility, and any vent or exhaust should be
fitted with an effective fabric filter or equivalent air pollution control
system; and •
Exposed earth should be
properly treated by compaction, turfing, hydroseeding, vegetation planting or
sealing with latex, vinyl, bitumen, shortcrete or other suitable surface
stabiliser within six months after the last construction activity on the
construction site or part of the construction site where the exposed earth
lies. |
Minimize
dust impact at the nearby sensitive receivers |
Contractor |
All
construction sites |
Construction phase |
* * ^ * ^ ^ ^ ^ ^ ^ N/A N/A N/A N/A N/A |
||||||||||
S3.8 |
D4 |
Implement regular dust monitoring under EM&A programme during the
construction stage. |
Monitoring of dust impact |
Contractor |
Selected representative
dust monitoring
station |
Construction phase |
^ |
||||||||||
Noise
Impact (Construction Phase) |
|||||||||||||||||
S4.9 |
N1 |
Implement the following good site management practices: •
Only well-maintained
plant should be operated on-site and plant should be serviced regularly
during the construction programme; •
Machines and plant (such
as trucks, cranes) 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, where possible, be orientated so that the noise is
directed away from nearby NSRs; silencers or mufflers on construction
equipment should be properly fitted and maintained during the construction
works; •
Mobile plant should be sited as far away from NSRs as possible and
practicable; •
Material stockpiles, mobile container site office and other structures should be effectively utilised,
where practicable, to screen noise from on-site construction activities. |
Control
construction airborne noise |
Contractor |
All
construction sites |
Construction phase |
^ ^ ^ ^ ^ |
||||||||||
S4.9 |
N2 |
Install temporary site hoarding (approx 2.4m
high) located on the site boundaries between noisy construction activities
and NSRs. The conditions of the hoardings shall be properly maintained
throughout the construction period. |
Reduce the
construction noise levels at low-level zone of NSRs through partial
screening. |
Contractor |
All
construction sites where practicable |
Construction phase |
^ |
||||||||||
S4.9 |
N3 |
Install movable noise barriers and full
enclosure and acoustic mat, screen the noisy plants including air compressor
and generator. |
Screen the
noisy plant items to be used at all construction sites |
Contractor |
All
construction sites where practicable |
Construction phase |
^ |
||||||||||
S4.9 |
N4 |
Use of ¡§Quiet¡¨ Plant and Working Methods |
Reduce the
noise levels of plant items |
Contractor |
All
construction sites where practicable |
Construction phase |
N/A |
||||||||||
S4.9 |
N5 |
Sequencing operation of construction plants
where practicable. |
Operate
sequentially within the same work site to reduce the construction airborne
noise |
Contractor |
All
construction sites where practicable |
Construction phase |
^ |
||||||||||
S4.9 |
N6 |
Implement a noise monitoring under EM&A
programme. |
Monitor the
construction noise levels at the selected representative locations |
Contractor |
Selected
representative noise monitoring stations |
Construction phase |
^ |
||||||||||
Water Quality
Impact (Construction Phase) |
|||||||||||||||||
S5.7 |
W1 |
Construction Runoff and Site Drainage In accordance with the Practice Note for Professional Persons on Construction
Site Drainage, Environmental Protection Department, 1994 (ProPECC PN 1/94),
construction phase mitigation measures should be provided and the Storm Water
Pollution Control Plan is given below. where appropriate, should include the following: Stormwater Pollution
Control Plan •
At the start of site
establishment, perimeter cut-off drains to direct off-site water around the
site should be constructed with internal drainage works and erosion and
sedimentation control facilities implemented. Channels (both temporary and
permanent drainage pipes and culverts), earth bunds or sand bag barriers
should be provided on site to direct stormwater to silt removal facilities.
The design of the temporary on-site drainage system will be undertaken by the
Contractor prior to the commencement of construction. •
Diversion of natural
stormwater should be provided as far as possible. The design of temporary
on-site drainage should prevent runoff going through site surface,
construction machinery and equipments in order to avoid or minimize polluted
runoff. Sedimentation tanks with sufficient capacity, constructed from pre-formed
individual cells of approximately
6 to 8m3 capacities, are recommended as a general mitigation measure
which can be used for settling surface runoff prior to disposal. The system
capacity shall be flexible and able to handle multiple inputs from a variety
of sources and suited to applications where the influent is pumped. •
The dikes or embankments
for flood protection should be implemented around the boundaries of earthwork
areas. Temporary ditches should be provided to facilitate the runoff
discharge into an appropriate watercourse, through a silt/sediment trap. The
silt/sediment traps should be incorporated in the permanent drainage channels
to enhance deposition rates. •
The design of efficient
silt removal facilities should be based on the guidelines in Appendix A1 of
ProPECC PN 1/94. The detailed design of the sand/silt traps should be
undertaken by the contractor prior to the commencement of construction. •
Construction works
should be programmed to minimize surface excavation works during the rainy
seasons (April to September). All exposed earth areas should be completed and
vegetated as soon as possible after earthworks have been completed. If excavation
of soil cannot be avoided during the rainy season, or at any
time of year when rainstorms are likely, exposed slope surfaces should be
covered by tarpaulin or other means. •
All drainage facilities
and erosion and sediment control structures should be regularly inspected and
maintained to ensure proper and efficient operation at all times and
particularly following rainstorms. Deposited silt and grit should be removed
regularly and disposed of by spreading evenly over stable, vegetated areas. •
Measures should be taken
to minimise the ingress of site drainage into excavations. If the excavation
of trenches in wet periods is necessary, it should be dug and backfilled in
short sections wherever practicable. Water pumped out from trenches or foundation
excavations should be discharged into storm drains via silt removal
facilities. •
All open stockpiles of
construction materials (for example, aggregates, sand and fill material) of
more than 50m3 should be covered with tarpaulin or similar fabric during
rainstorms. Measures should be taken to prevent the washing away of
construction materials, soil, silt or debris into any drainage system. •
Manholes (including
newly constructed ones) should always be adequately covered and temporarily
sealed so as to prevent silt, construction materials or debris being washed
into the drainage system and storm runoff being directed into foul sewers. •
Precautions to be taken
at any time of year when rainstorms are likely, actions to be taken when a
rainstorm is imminent or forecasted, and actions to be taken during or after
rainstorms are summarized in Appendix A2 of ProPECC PN 1/94. Particular attention
should be paid to the control of silty surface runoff during storm events. •
All vehicles and plant
should be cleaned before leaving a construction site to ensure no earth, mud,
debris and the like is deposited by them on roads. An adequately designed and
sited wheel washing facilities should be provided at every construction site
exit where practicable. Wash-water should have sand and silt settled out and
removed at least on a weekly basis to ensure the continued efficiency of the
process. The section of access road leading to, and exiting from, the
wheel-wash bay to the public road should be paved with sufficient backfall
toward the wheel-wash bay to prevent vehicle tracking of soil and silty water
to public roads and drains. •
Oil interceptors should
be provided in the drainage system downstream of any oil/fuel pollution
sources. The oil interceptors should be emptied and cleaned regularly to
prevent the release of oil and grease into the storm water drainage system
after accidental spillage. A bypass should be provided for the oil interceptors
to prevent flushing during heavy rain. •
Construction solid
waste, debris and rubbish on site should be collected, handled and disposed
of properly to avoid water quality impacts. •
All fuel tanks and storage
areas should be provided with locks and sited on sealed areas, within bunds
of a capacity equal to 110% of the storage capacity of the largest tank to
prevent spilled fuel oils from reaching water sensitive receivers nearby. •
Regular environmental
audit on the construction site should be carried out in order to prevent any
malpractices. Notices should be posted at conspicuous locations to remind the
workers not to discharge any sewage or wastewater into the meander, wetlands
and fish ponds. |
Control construction
runoff |
Contractor |
All
construction sites |
Construction phase |
* ^ ^ ^ N/A ^ ^ * ^ ^ ^ N/A ^ ^ ^ |
||||||||||
S5.7 |
W2 |
Stream Diversion •
In order to prevent sediment transport during
riverbank works, deployment of silt curtain should be implemented, especially
when construction works encroach or occur in close distance to water body. It
is recommended to carry out all the riverbank works and diversion works
within a cofferdam or diaphragm wall and the work areas on riverbed should be
kept in dry condition. |
Minimize
water quality impact due to stream diversion |
Contractor |
All streams
that required diversion |
Construction phase |
N/A |
||||||||||
S5.7 |
W3 |
Groundwater from Contaminated Area •
For other inaccessible sites, site
investigation is required when they are resumed and handed over to the
Project Proponent to identify if contaminated groundwater is found. •
If the investigation results indicated that the
groundwater to be generated from construction works would be contaminated,
the contaminated groundwater should be either discharged into recharged
wells, or properly treated in compliance with the requirements of Technical
Memorandum on Standards for Effluents Discharged into Drainage on Sewerage
Systems, Inland and Coastal Waters. •
If recharged well method were used, the
groundwater quality in the recharged well should not be affected by
recharging operation, i.e. the pollution levels of the recharged groundwater
should not be higher than that in the recharging wells. •
If treatment and discharge method were used,
the design of wastewater treatment facilities, such as active carbon and
petrol interceptor, should be submitted to the EPD and a discharge license
should be obtained under the WPCO through the Regional Offices of EPD. |
Minimize
water quality impact due to potential groundwater from contaminated area |
Contractor |
All
identified groundwater- contaminated areas |
Construction phase |
N/A N/A N/A N/A |
||||||||||
S5.7 |
W4 |
Sewage
from Workforce Portable
chemical toilets and sewage holding tanks should be provided for handling the
construction sewage generated by the workforce. A licensed Contractor should
be employed to provide appropriate and adequate portable toilets and be
responsible for appropriate disposal and maintenance. Notices should be posted at conspicuous locations to remind the workers not to discharge any sewage or wastewater into the nearby environment during the construction phase of the Project. Regular environmental audit on the construction site should be conducted in order to provide an effective control of any malpractices and achieve continual improvement of environmental performance on site. It is anticipated that sewage generation during the construction phase of the Project would not cause water quality impact after undertaking all required measures. |
Handling of
site sewage |
Contractor |
All
construction sites |
Construction Phase |
^ |
||||||||||
Waste
Management (Construction Waste) |
|||||||||||||||||
S7.6 |
WM1 |
Waste
Reduction Measures Waste reduction is best achieved at the planning and design phase, as
well as by ensuring the implementation of good site practices. The following
recommendations are proposed to achieve reduction: •
segregate and store different types of waste
in different containers, skip or
stockpiles to enhance reuse or recycling of materials and their proper
disposal; •
proper storage and site practices to minimize
the potential for damage and contamination of construction materials; •
plan and stock construction materials carefully
to minimize amount of waste generated and avoid
unnecessary generation of waste; •
sort out demolition debris and excavated
materials from demolition works to recover
reusable/recyclable portions (i.e. soil, broken concrete, metal etc); •
provide training to workers on the importance
of appropriate waste management procedures, including waste reduction, reuse
and recycling. |
Reduce
waste generation |
Contractor |
All
construction sites where practicable |
Prior to
the commencement of construction |
^ ^ ^ N/A ^ |
||||||||||
S7.6 |
WM2 |
Prepare Waste Management Plan and submit to the Engineer for approval |
Minimize
waste generation during construction |
Contractor |
All
construction sites |
Construction phase |
N/A |
||||||||||
S7.6 |
WM3 |
Good
Site Practice The following good site practices are recommended throughout the construction
activities: •
Nomination of an approved personnel, such as
a site manager, to be responsible for the implementation of good site
practices, arrangements for collection and effective disposal to an appropriate
facility, of all wastes generated at the site; •
Training of site personnel in site
cleanliness, appropriate waste management procedures and concepts of waste
reduction, reuse and recycling; •
Provision of sufficient waste disposal points
and regular collection for disposal; •
Appropriate measures to minimise windblown
litter and dust during transportation of waste by either covering trucks or
by transporting wastes in enclosed containers; •
Regular cleaning and maintenance programme
for drainage systems, sumps and oil interceptors; |
Minimize
waste generation during construction |
Contractor |
All
construction sites |
Construction phase |
^ ^ ^ ^ ^ |
||||||||||
S7.6 |
WM4 |
Storage
of Waste The following recommendation should be implemented to minimize the impacts: •
Waste such as soil should be handled and
stored well to ensure secure
containment; •
Stockpiling area should be provided with
covers and water spraying
system to prevent materials from wind-blown or being washed away; •
Different locations should be designated to
stockpile each material to enhance reuse; |
Minimize
waste impacts from storage |
Contractor |
All
construction sites |
Construction phase |
^ ^ ^ |
||||||||||
S7.6 |
WM5 |
Collection
and Transportation of Waste The following recommendation should be implemented to minimize the impacts: •
Remove waste in timely manner; •
Employ the trucks with cover or enclosed
containers for waste transportation; •
Obtain relevant waste disposal permits from
the appropriate authorities; and •
Disposal of waste should be done at licensed
waste disposal facilities. |
Minimize
waste impact from storage |
Contractor |
All
construction sites |
Construction phase |
^ ^ ^ ^ |
||||||||||
S7.6 |
WM6 |
Excavated
and C&D Material Wherever practicable, C&D materials should be segregated from other
wastes to avoid contamination and ensure acceptability at Public Fill Reception
Facilities areas or reclamation sites. The following mitigation measures
should be implemented in handling the excavated and C&D materials: •
Maintain temporary stockpiles and reuse
excavated fill material for backfilling; •
Carry out on-site sorting; •
Deliver surplus artificial hard materials to
Tuen Mun Area 38 recycling plant or its successor for recycling into
subsequent useful products; •
Make provisions in the Contract documents to
allow and promote the use of recycled aggregates where appropriate; and •
Implement a recording system for the amount
of waste generated, recycled and disposed of for checking; Standard formwork
should be used as far as practicable in order to minimize the arising of
C&D waste. The use of more durable formwork (e.g. metal hoarding) or
plastic facing should be encouraged in order to enhance the possibility of
recycling. The purchasing of construction materials should be carefully
planned in order to avoid over ordering and wastage. Wheel wash facilities
have to be provided at the site entrance before the trucks leaving the works
area. |
Minimize
waste impacts from excavated and C&D material |
Contractor |
All
construction sites |
Construction phase |
^ ^ N/A N/A N/A ^ N/A ^ |
||||||||||
S7.6 |
WM7 |
Contaminated
Soil As a precaution, it is recommended that
standard good site practice should be implemented during the construction
phase to minimize any potential exposure to contaminated soils or
groundwater. The details of mitigation measures to minimize the potential
environmental implications arising from the handling of contaminated
materials refer to Land Contamination Section. |
Remediate
contaminated soil |
Contractor |
All
construction sites where applicable |
Construction
phase |
^ |
||||||||||
S7.6 |
WM8 |
Chemical
Waste If chemical
wastes are produced at the construction site, the Contractors should register
with EPD as chemical waste producers. Chemical wastes should be stored in
appropriate containers and collected by a licensed chemical waste Contractor.
Chemical wastes (e.g. spent lubricant oil) should be recycled at an
appropriate facility as far as possible, while the chemical waste that cannot
be recycled should be disposed of at either the Chemical Waste Treatment Centre,
or another licensed facility, in accordance with the Waste Disposal (Chemical
Waste) (General) Regulation. |
Control the
chemical waste and ensure proper storage, handling and disposal |
Contractor |
All
construction sites |
Construction
phase |
* |
||||||||||
S7.6 |
WM9 |
General
Waste •
General refuse
should be stored in enclosed bins separately from construction and chemical
wastes. Recycling bins should also be placed to encourage recycling. •
Preferably enclosed
and covered areas should be provided for general refuse collection and
routine cleaning for these areas should also be implemented to keep areas
clean. •
A reputable waste
collector should be employed to remove general refuse on a daily basis. |
Minimize
production of the general refuse and avoid odour, pest and litter impacts |
Contractor |
All
construction sites |
Construction
phase |
N/A ^ N/A |
||||||||||
S7.6 |
WM10 |
Sewage •
The WMP should
document the locations and number of portable chemical toilets depending on
the number of workers, land availability, site condition and activities. •
Regularly collection
by licensed collectors should be arranged to minimize potential environmental
impacts. |
Minimize
production of sewage impacts |
Contractor |
All
construction sites |
Construction
phase |
N/A N/A |
||||||||||
S7.6 |
WM11 |
Topsoil reuse ¡V Topsoil,
where identified, should be stripped and stored for re-use in the
construction of the soft landscape works, where practical. This is considered
a general measure for good site practice. |
Good site
practice |
Contractor/
Project Proponent |
Onsite |
Construction
phase |
N/A |
||||||||||
Land
Contamination |
|||||||||||||||||
S 8.4 |
LC2 |
Detailed
site investigation (SI) for all inaccessible potentially contaminated
sites in 2 NDAs |
Verify
the land contamination
potential before
the commencement of
construction |
Project Proponent Detailed Design Consultant Contractor |
All
inaccessible potentially contaminated
sites in 2 NDAs as
listed in the CAP |
After the
land is resumed and handed over to the Project Proponent |
* |
||||||||||
S 8.5 |
LC3 |
Preparation
and submission of supplementary Contamination Assessment
Report (CAR) and Remediation Action Plan (RAP) for all
inaccessible potentially contaminated sites in 2 NDAs to EPD for
agreement if land contamination is confirmed |
Present
the findings of SI and
evaluate the potential environmental
and human health
impacts Recommend
appropriate mitigation
measures for the contaminated
soil and groundwater
identified in the
assessment if remediation is required |
Project Proponent/ Detailed Design Consultant |
All
inaccessible potentially contaminated
sites in 2 NDAs as listed in the CAP |
Prior
to the commencement
of any proposed construction works
if land contamination is
confirmed and
remediation is required |
* |
||||||||||
S 8.5 |
LC4 |
Preparation
and submission of Remediation Report to EPD for agreement |
Demonstrate
that the decontamination
work is adequate
and is carried out in
accordance with the endorsed
supplementary CAR
and RAP |
Project Proponent/ Detailed Design Consultant |
All
inaccessible potentially contaminated
sites in 2
NDAs as listed in the CAP |
Prior
to the commencement
of any proposed construction works
if land contamination is
confirmed and
remediation is required |
N/A |
||||||||||
S 8.6 |
LC5 |
Re-appraisal
of surveyed sites (if they become part of the land requirement for NDA
development) that were not identified as potentially contaminated or could
not be accessed for visual inspection during the site survey |
Verify
the land contamination potential due to potential change of land uses before
the commencement of construction |
Project Proponent/ Detailed Design Consultant |
All
surveyed sites (if they become part of the land requirement for NDA
development (that were not identified as potentially contaminated or could
not be accessed for visual inspection during the site survey as listed in the
CAP |
After
the land is resumed and handed over to the Project Proponent. |
N/A |
||||||||||
S 8.7.2 and Appendix 8.4 |
LC6 |
Treatment
of arsenic-containing soil ¡§Solidification/Stabilization¡¨
(S/S) treatment method was proposed for the treatment of arsenic-containing
soil. Toxicity Characteristic Leaching
Procedure (TCLP) test should be undertaken after S/S in order to ensure that
the contaminant will not leach to the environment. Unconfined Compressive
Strength (UCS) test should be conducted, and not less than 1MPa should be met
prior to the backfilling or stockpiled for future reuse within the study
area. |
To
treat the arsenic containing soil |
Government Developer/ Contractor |
KTN
NDA |
Prior
to commencement of construction works
within KTN
NDA |
N/A |
||||||||||
S
8.7.2 and Appendix 8.4 |
LC7 |
Excavation and Transportation •
Excavation profiles must
be properly designed and executed with attention to the relevant requirements for environment, health and safety; •
In case the soil to be
excavated is situated beneath the groundwater table, it may be necessary to
lower the groundwater table; •
Excavation should be
carried out during dry season as far as possible to minimize runoff from excavated soils; •
Stockpiling site(s)
should be lined with impermeable sheeting and bunded. Stockpiles should be properly covered by impermeable sheeting to reduce dust emission during dry season or contaminated run-off during rainy season. Watering should be avoided on stockpiles of soil to minimize runoff; •
Supply of suitable
backfill material after excavation, if require; Vehicles containing any excavated materials should be suitably covered to limit potential dust emissions or run-off, and truck
bodies and tailgates should be sealed to prevent any discharge during
transport or during wet season; •
Speed control for the
trucks carrying excavated materials should be enforced; and Vehicle wheel
washing facilities at the site¡¦s exit points should be established and used. |
To
minimize the potential environmental
impacts arising
from the handling of contaminated
materials |
Contractor |
KTN
NDA |
Prior
to commencement of construction works
within KTN
NDA |
N/A |
||||||||||
S
8.7.2 and Appendix 8.4 |
LC8 |
Solidification/Stabilization •
The loading, unloading,
handling, transfer or storage of cement should be carried out in an enclosed system; •
Mixing process and other
associated material handling activities should be properly scheduled to minimize potential noise impact and dust emission; •
The mixing facilities
should be sited as far apart as practicable from the nearby noise sensitive receivers; •
Mixing of soil and
cement / water / other additive(s) should be
undertaken at a solidification plant to minimize the potential for leaching; •
Runoff from the
solidification / stabilization area should be prevented by constructing a concrete bund along the perimeter of the solidification / stabilization area; •
If stockpile of treated
soil is required, the stockpiling site(s) should be lined with
impermeable sheeting and bunded. Stockpiles should be
properly covered by impermeable sheeting to reduce dust
emission during dry season or site run-off during rainy season; and If necessary, there should be clear and separated areas for stockpiling of untreated and treated materials. |
To
minimize the potential environmental
impacts arising
from the handling of contaminated
materials |
Contractor |
KTN
NDA |
The
course of treatment |
N/A |
||||||||||
S
8.7.2 and Appendix 8.4 |
LC9 |
Safety Measures •
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 zones requiring treatment and clean zones; •
Maintain
a hygienic working environment; •
Avoid dust generation; •
Provide face and
respiratory protection gear to site workers if necessary; •
Provide personal
protective clothing (e.g. chemical resistant •
jackboot, liquid tight
gloves) to site workers if necessary; •
Provide first aid
training and materials to site worker; •
Bulk earth moving
equipment should be utilized as much as possible to minimize worker Eating,
drinking and smoking should not be allowed in the excavation
areas and treatment area to avoid inadvertent ingestion of
arsenic containing soil. |
To
minimize the potential adverse
effects on health and
safety of construction workers |
Contractor |
KTN
NDA |
The
course of treatment |
N/A |
||||||||||
Landfill
Gas Hazard |
|||||||||||||||||
S10.6 |
LFG1 |
•
Underground rooms or void should be avoided
as far as practicable in the proposed developments within the Consultation
Zone and should be avoided totally in the proposed developments within the
MTLL. •
Buildings or structures within the MTLL
should be at ground level with raised floor slabs which are less prone to gas
ingress. •
For the high risk category, the use of active
control of gas, including barriers and detection systems are recommended. These
measures include the control of gas by mechanical means e.g. ventilation of
spaces with air to dilute gas, or extraction of gas using fans or blowers. •
For the low risk category, the provision of
barriers to the movement of gas is recommended. Measures recommended include
the use of membranes in floors or walls, or in trenches, coupled with high
permeability vents such as nofines gravel in trenches or voids/permeable
layers below structures. •
The need and practicality of incorporating
such measures should be reviewed in the detailed Qualitative LFG Hazards Assessment
(QLFGHA) during the detailed design stage for developments within the 250m
Consultation Zone and within MTLL. Recommendations on the detailed
precautionary and protection measures to be adopted should be given in the QLFGHA. •
The design and construction method of the
proposed development within MTLL (i.e. the proposed recreational area in site
E1-1) should be provided to EPD for agreement in the design stage to ensure
compatibility with the landfill restoration facilities and aftercare works
within MTLL, such that these facilities and works will not be affected by the
construction or operation of the proposed development. |
To minimize
the risk of LFG hazards to
occupants within MTLL and
its 250m Consultation
Zone |
Government
/ Developer/ Detailed Design Consultant within
MTLL and
its 250m Consultation Zone |
Buildings
within MTLL and its
250m Consultation
Zone |
Detailed design
phase |
N/A |
||||||||||
S10.6 |
LFG2 |
•
During all works, safety procedures should be
implemented to minimize the risks of fires and explosions, asphyxiation of workers
(especially in confined space) and toxicity effects resulting from contact
with contaminated soils and groundwater. •
Safety officers, specifically trained with
regard to LFG and leachate related hazards and the appropriate actions to
take in adverse circumstances, should be present on all worksites throughout
the works. •
All personnel who work on site and all
visitors to the site should be made aware of the possibility of ignition of
gas in the vicinity of the works, the possible presence of contaminated water
and the need to avoid physical contact with it. •
Those staff who work in, or have
responsibility for ¡§at risk¡¨ areas, including bore pilling and excavation
works, should receive appropriate training on working in areas susceptible to
LFG. •
Enhanced personal hygiene practices including
washing thoroughly after working and eating only in ¡§clean¡¨ areas should be
adopted where contact may have been made with any groundwater which is
thought to be contaminated with leachate. •
Any offices / quarters set up on site should
take precautions against LFG ingress, such as being raised off the ground. Other
storage premizes, e.g. shipping containers, where this is not possible should
be well ventilated prior to entry. •
Adequate precautions to prevent the
accumulation of LFG under site buildings and within storage shed should be
taken by raising buildings off the ground where appropriate and¡§airing¡¨ storage containers prior to
entry by personnel and ensuring adequate ventilation at all times. •
Smoking and naked flames should be prohibited
within confined spaces. ¡§No Smoking¡¨ and ¡§No Naked Flame¡¨ notices in Chinese
and English should be posted prominently around the construction site. Safety
notices should be posted warning of the potential hazards. •
Welding, flame-cutting or other hot works may
only be carried out in confined spaces when controlled by a ¡§permit to work¡¨ procedure,
properly authorized by the Safety Officer. The permit to work procedure
should set down clearly the requirements for continuous monitoring of
methane, carbon dioxide and oxygen throughout the period during which the hot
works are in progress. The procedure should also require the presence of an
appropriately qualified person who shall be responsible for reviewing the gas
measurements as they are made, and who shall have executive responsibility
for suspending the work in the event of unacceptable or hazardous conditions.
Only those workers who are appropriately trained and fully aware of the
potentially hazardous conditions which may arise should be permitted to carry
out hot works in confined areas. •
During the construction works, adequate fire
extinguishers and breathing apparatus sets should be made available on site and
appropriate training given in their use. •
Ongoing gas monitoring should be considered
for offices, stores etc set up on site. |
To minimize
the risk of LFG hazards to
the staff and visitors
within MTLL and its 250m Consultation Zone |
Contractor |
Construction
sites within MTLL
and its 250m
Consultation Zone |
Construction phase |
N/A |
||||||||||
S10.6 |
LFG3 |
Utility
Companies •
The developers should make the utility
companies aware of the location and features of the site within the
Consultation Zone during the respective detailed design stage as part of the QLFGHA. •
The utilities companies should have a
responsibility to train and ensure their staff to take appropriate
precautions at all times when entering enclosed spaces or plant rooms. •
Should utility installation be required in
site E1-1, the developers should make the utility companies aware of the potential
constraints imposed by the landfill restoration facilities and aftercare
works to ensure these facilities and works will remain unaffected.
Appropriate precautionary measures against landfill gas should also be taken
should utility installation be required within the MTLL. Building
Management •
The management committee of the building
estate will hold a special responsibility to ensure that the occupants of the
building, its staff and maintenance workers are protected from LFG and that
visitors to the site are also made aware as to the dangers and the
precautions required to be taken. •
Of primary importance to satisfactorily
upholding this responsibility will be to ensure that strict procedures for maintaining
control over all temporary and /or permanent works proposed at the site are
reviewed with regard to the LFG hazard. This needs to be accompanied by a comprehensive
contingency plan in case of incidents, including liaison with EPD officers,
Fire Services Department, Landfill Restoration Contractors and others, as
necessary. •
All construction and maintenance (including
utilities) personnel working at the site should be made aware of the hazards
of LFG and its possible presence on site. This should be achieved through a
combination of posting warning signs in prominent places and also by access
to detailed information on LFG hazards and the designs and procedural means
by which these hazards are being minimized on site. In addition, entry to
confined spaces such as refuse/store rooms, drainage manholes etc. should be
preceded by a period of ¡§airing¡¨ the space by opening the door widely
allowing fresh air to enter. Where appropriate, monitoring of gas should also
precede entry. •
Any proposed modifications or additions to
the building structure should be subject to a further assessment of LFG hazard,
particularly in areas where a gas membrane has been installed. Any
penetrations of the membrane must be repaired as soon as possible after
detection or works completion using similar products. •
The building management company should also
make arrangement with Landfill Restoration Contractor so that they are
advised of all situations which may potentially threaten the safety of the
building occupants resulting from any accidents or failures at the landfill
site. The building management company should also have available suitable gas
monitoring equipment for any ad hoc investigations necessary relating to LFG
and be in a position to undertake any future routine monitoring of gas which
may be considered necessary soloing completion of the defects correction
period. •
To ensure that all the above protection and
precautionary measures and issues pertaining to LFG are properly and consistently
addressed by future users and owners of the site, it is recommended that a
comprehensive LFG hazard management
system be developed by the owner of the building or its property management
agency. The system should be developed by the developers of the sites as part
of the QLFGHA before the occupation of the building and implemented during
its operational phase. |
To minimize
the risk of LFG hazards to
the occupants, maintenance
personnel, visitors
and other users within MTLL
and its 250m Consultation
Zone |
Government
/ Developer within MTLL and its
250m Consultation Zone |
Buildings
within MTLL and its
250m Consultation
Zone |
Operation phase |
N/A |
||||||||||
Cultural
Heritage (Pre-construction Phase) |
|||||||||||||||||
S11.6.1 |
CH1 |
Undertaking Further
Archaeological Survey to Cover the Outstanding Areas Further archaeological
surveys to cover the outstanding areas of the not-yet-surveyed-area with medium
archaeological potential located in the areas with proposed development as
presented in Figure 11.9 should be implemented after land resumption to
confirm and verify the findings of the EIA. The survey should be conducted by a
professional archaeologist and prior to fieldwork commencement, the
archaeologist should obtain a Licence to Excavate and Search for Antiquities
from the Authority under the AM Ordinance. It should be noted that the scope of
further archaeological survey is based on the current proposed
alignment. Any additional works
areas which have not been covered by the current archaeological impact
assessment should be covered as soon as possible. Subject to the findings of the
archaeological survey to be conducted after land resumption, additional
mitigation measures would be designed and implemented before the commencement
of construction works to mitigate the adverse impact. |
To confirm
and verify the findings of the EIA |
Project
Proponent/ Contractor/ Qualified Archaeologist |
In the not-yet-surveyed-areas
with medium archaeological potential located in the areas within Areas D1-11,
A3-5, A3-6, B1-1, and B1-7, |
After land
resumption but before construction
|
N/A |
||||||||||
S11.6.1 |
CH2 |
Undertaking
Survey-cum-Rescue Excavation A Survey-cum-Rescue Excavation
should be conducted after land resumption and before the commencement of
construction works to define the precise archaeological deposits extent and
to preserve the archaeological resources by record. The excavation should be conducted by
a professional archaeologist and prior to fieldwork commencement, the
archaeologist should obtain a Licence to Excavate and Search for Antiquities
from the Authority under the AM Ordinance. |
To define
the precise archaeological deposits extent and to preserve the archaeological
resources as far as possible |
Project
Proponent/ Contractor/ Qualified Archaeologist |
In KTN NDA,
for Site 3 and In FLN NDA for Site 5. |
After land
resumption but before construction commencement of the zone |
N/A |
||||||||||
S11.6.1 |
CH3 |
Undertaking
Preservation in-situ for Site 7 Preservation in-situ
of the cultivation deposits in Site 7 is proposed. If disturbance to the site by the
design of the Central Park is unavoidable, further archaeological survey
should be conducted after land resumption prior to the pre-construction stage
to assess the feasibility to incorporate Site 7 into the design of the
development plan of the proposed zone. Appropriate followup actions,
including preservation of the significant archaeological deposits in-situ in
the Central Park, would then be considered with the consent of AMO. The recommended
mitigation measure of preservation in-situ with further archaeological survey
should be conducted by a professional archaeologist and prior to fieldwork
commencement, the archaeologist should obtain a Licence to Excavate and
Search for Antiquities from the Authority under the AM Ordinance. |
To preserve
the archaeological resources as far as possible. |
Project
Proponent/ Contractor/ Qualified Archaeologist |
Site 7 in FLN
NDA |
After land
resumption prior to preconstruction stage of the proposed Central Park (Area
C2-8, Zoning O) |
N/A |
||||||||||
S11.6.1 |
CH4 |
Undertaking Induction
Training Induction training
should be provided to the construction Contractor before the commencement of
the excavation works in Spots A, D, F to H. An induction will be conducted as part
of the environmental health and safety induction programme to all site staff
before they are deployed on site.
The induction will include an introduction on the historical
development of the Site, the possible archaeological remains that may be
encountered during ground excavation works as well as the reporting
procedures in case suspected archaeological remains are identified. A set of the presentation material (in
the form of power point presentation) with content details will be prepared
by an archaeologist and submitted to AMO for reference and record purpose.
The first induction briefing will be video recorded and it will be used as
induction briefing material for new site staff. |
To preserve
the archaeological resources as far as possible |
Project
Proponent/ Contractor/ Qualified Archaeologist |
Spots A, D,
F to H |
Before the
commencement of the excavation works and before site staff are deployed on
site |
N/A |
||||||||||
S11.6.1 |
CH5 |
Undertaking
Archaeological Impact Assessment before Construction at A1 It is recommended that
an Archaeological Impact Assessment to be conducted in the impacted area in
Area B1-8 and B1-9 at A1 (Sheung Shui Wa Shan Site of Archaeological
Interest) after land resumption and before construction when detail
construction work information is available to determine the need for further archaeological
follow up actions. |
To define
the precise archaeological deposits extent and to preserve the archaeological
resources as far as possible |
Project
Proponent/ Contractor/ Qualified Archaeologist |
Area B1-8
and B1-9 zoned as R4 and R3 in A1
|
After land
resumption but before construction |
N/A |
||||||||||
S11.6.1 |
CH6 |
Undertaking
Archaeological Impact Assessment before Construction within A1 but except
Area B1-8 and B1-9 Should there be any
development work within the Sheung Shui Wa Shan Site of Archaeological
Interest, it is recommended that an Archaeological Impact Assessment is
required after land resumption and before construction when detail
construction work information is available to determine the need for further
archaeological follow up actions. |
To define
the precise archaeological deposits extent and to preserve the archaeological
resources as far as possible. |
Project
Proponent/ Contractor/ Qualified Archaeologist |
Area within
A1 except Area B1-8 and B1-9 in R4 &R3 zoning |
After land
resumption but before construction |
N/A |
||||||||||
S11.6.2 |
CH7 |
Undertaking baseline
condition survey and baseline vibration impact assessment In case any potential
vibration impact on any nearby built heritage features are identified during
the pre-construction stage of the Project, prior to commencement of construction
works, a baseline condition survey and baseline vibration impact assessment
should be conducted by a qualified building surveyor or a qualified
structural engineer to define the vibration limit (a vibration limit at
7.5mm/s could be adopted for graded historic buildings) and to evaluate if
construction vibration monitoring and structural strengthening measures are
required during construction phase so as to ensure the construction
performance meets with the vibration standard stated in the EIA report. The condition survey of graded
historic building should be submitted to AMO for information. |
To minimize
the vibration impacts during preconstruction stage on any identified
potential vibration impacted built heritage features |
Project
Proponent/ Contractor |
G303 and
G308 |
Preconstruction
stage before commencement of construction works during Schedule 3 study |
N/A |
||||||||||
S11.6.2 |
CH8 |
Undertaking
baseline condition survey and baseline vibration impact assessment In case any
potential vibration impact on any nearby built heritage features are
identified during the pre-construction stage of the Project, prior to
commencement of construction works, a baseline condition survey and baseline
vibration impact assessment should be conducted by a qualified building
surveyor or a qualified structural engineer to define the vibration limit (a
vibration limit at 7.5mm/s and 15mm/s could be adopted for graded historic
buildings and historic buildings respectively) and to evaluate if
construction vibration monitoring and structural strengthening measures are
required during construction phase so as to ensure the construction
performance meets with the vibration standard
stated in the EIA report. The
condition survey of graded historic building should be submitted to AMO for
information. |
To minimize
the vibration impacts during preconstruction stage on any identified
potential vibration impacted built heritage features |
Project
Proponent/ Contractor |
KT57, FL05,
FL18, and FL2 |
Preconstruction
stage before commenceme nt of construction works |
N/A |
||||||||||
S11.6.2 |
CH9 |
Conducting
Photographic and Cartographic Records Prior to Removal/Relocation of Impacted
Built Heritages Prior to
removal/relocation of the directly impacted historical buildings and
cultural/historical landscape features, photographic and cartographic records
should be conducted to preserve them by record. Liaison with and obtaining agreement
from the descendants of these features will be carried out the Project
Proponent. |
To preserve
the directly impacted sites by record prior to their removal /
relocation |
Project
Proponent/ Contractor |
Ancillary
structures of G303, HKT01, HKT02, Entrance Gate of HKT03, HKT04, KT01 to
KT10, KT13, KT36, KT39, KT40, KT41, KT43, KT45, KT47, KT50, KT54, KT62 to KT63, KT69,
FL01, FL16, and FL35 |
Prior to
Removal / Relocation of features before commenceme nt of construction works
during Schedule 3 study |
N/A |
||||||||||
S11.6.2 |
CH10 |
Conducting
Photographic and Cartographic Records Prior to Removal/Relocation of Impacted
Built Heritages |
To preserve
the directly impacted sites by record prior to their removal / relocation |
Project
Proponent/ Contractor |
KT12 and
KT61 |
Prior to
Removal / Relocation of features before commencement of construction works |
N/A |
||||||||||
S11.6.2 |
CH11 |
Relocation of Built
Heritages Relocation of built heritages to a reasonable location nearby may
be required. |
To preserve
the directly impacted sites by relocation |
Project
Proponent/ Contractor |
HKT01,
HKT02, Entrance Gate of HKT03 |
After the
photographic and cartographic records and before commencement of construction
works |
N/A |
||||||||||
S11.6.2 |
CH12 |
Drainage System and
Access Route Design For the retained built heritage items in developable
area, drainage system and access route would be designed to prevent the persevered
flooding and maintain the accessibility to the built heritage. |
To prevent
the persevered flooding and maintain the accessibility to the built heritage |
Contractor
/Detailed Design consultant |
The
retained built heritage items |
Pre-construction
phase |
N/A |
||||||||||
Cultural
Heritage (Construction Phase) |
|||||||||||||||||
S11.6.1 |
CH13 |
Inform Upon Archaeological Discovery Pursuant to the Antiquities and Monuments
Ordinance, the construction Contractor should inform the AMO immediately in
case of discovery of antiquities or supposed antiquities in the course of
excavation works in construction phase. |
Special
attention should be given to areas evaluated to have archaeological potential
or significance. |
Contractor |
All soil
excavation works |
Immediately
upon discovery during excavation works |
N/A |
||||||||||
S11.6.2 |
CH14 |
Watertable Monitoring Since the construction works and development
activities may induce change in the watertable. It is recommended the
Contractor should ensure that the change of watertable induced by the
construction works and development activities will not result in settlement
of built heritage. |
To minimize
the potential impacts to the built heritage items by the change of watertable
induced by the works during the Construction phase |
Contractor |
Within NDAs
|
Construction
phase |
N/A |
||||||||||
S11.6.2 |
CH15 |
Conducting Construction Vibration Monitoring
and Structural Strengthening Measures Construction vibration monitoring and
structural strengthening measures should be conducted during Construction
phase based on the assessment result of baseline condition survey and
baseline vibration impact assessment, so as to ensure the construction
performance meets with the vibration standard stated in the EIA report. |
To minimize
the potential impacts during Construction phase on any identified potential
vibration impacted built heritage features |
Contractor |
Identified
potential vibration impacted built heritage features |
Construction
phase, with details specified in baseline condition survey and baseline
vibration impact assessment |
N/A |
||||||||||
Landscape and Visual
Impact (Detailed Design, Prior to Construction, Construction and Operation
Phases) |
|||||||||||||||||
S.12.9 |
LV1 |
General Good Practice
Measures - For areas unavoidably disturbed by the Project on a short term
basis e.g. works areas, the general principle to try and restore these to
their former state to suit future land use, should be adhered to. With regard to
topsoil, where identified, it should be stripped, treated appropriately, and
where suitable and practical stored for re-use in the construction of the
soft landscape works such as roadside amenity strips, and open space sites. |
|
Detailed
design consultant/ Contractor |
Throughout
NDAs, |
Prior to
Construction, Construction & for all planting, this should be installed
as the areas become available, to achieve early establishment |
N/A |
||||||||||
S.12.9 MM1 |
LV2 |
Minimum
Topographical Change ¡VTo minimize landscape and visual impacts, the footprint
and elevation of such elements should be optimized to reduce topographical/ landform
changes, as well as reduce land take and interference with natural terrain.
Where there is a need to significantly cut into the existing landform,
retaining walls should be considered as well as cut slopes, to minimize
landform changes and land resumption, while also considering visual amenity.
Earthworks and engineered slopes should be designed to be a visually
interesting landform, compatible with the surrounding landscape and to mimic
the natural contouring and terrain e.g. introduction and continuation of
natural features such as spurs and ridges where appropriate, to support
assimilation with the hillside setting. |
Reduce
topographical changes and minimize land resumption |
Government
/ Detailed Design Consultant/ Contractor |
Throughout
NDAs, particularly for reservoirs |
Prior to
Construction |
N/A |
||||||||||
S.12.9 MM2 |
LV3 |
Detailed Design (Visual) ¡VThe footprint and massing of development components and the works area should also be kept to a practical minimum and the detailed design of development components for Construction phase should follow the Sustainable Building Design Guidelines. The form, textures, finishes and colours of the proposed development components should aim to be compatible with the existing surroundings. To improve visual amenity designs should be aesthetically pleasing and treatment of structures also improve visual amenity. For example, natural building materials such as stone and timber, should be considered for architectural features, and light earthy tone colours such as shades of green, shades of grey, shades of brown and off-white should also be considered to reduce the visibility of the development components, including all roadwork, buildings and noise barriers. In addition, the design of structures should consider green roofs were feasible, following stated guidelines. All Noise barriers, particularly noise barriers but also any barriers proposed for ecological impact mitigation, should be kept to a practical minimum, and be of such a designed as to integrate as well as possible into the surrounding visual context and be as low as practical to minimize blocking views. Noise barrier design, including vertical, cantilever or curved, and noise enclosures including semi-enclosure and full enclosure, at grade and/ or elevated, should follow the guidelines stated. Construction time frame should also be considered and designs seek to keep it to a practical minimum. |
Improve
visual amenity of the new buildings, NDAs in general and integrate as best
possible into the surrounding landscape |
Detailed
Design Consultant |
Throughout
NDAs |
Prior to Construction |
N/A |
||||||||||
S12.9
MM14.4 |
LV 4 |
Avoid affecting Watercourses ¡V In the
detailed design, consideration should be made of watercourses, to minimize
any impacts e.g. at new bridge crossings, viaducts, road alignment etc.
Guidelines stated should be followed. For example, for the stream at Siu Hang San
Tsuen in FLN NDA, much of the stream is located underneath the viaduct for
the proposed Fanling Bypass. In order to avoid impacts to the stream, the
detailed final design of the viaduct should follow guidelines and ensure that
no viaduct footings or other structures are placed in the stream. Bridges and box culverts should also be used
to minimize the necessity of watercourse modification and protect the
watercourses where necessary. |
Avoid
direct impacts to watercourses |
Detailed
Design Consultant/ Contractor |
All
watercourses, particularly the
stream at Siu Hang San Tsuen that will flow under the Fanling Bypass Eastern
Section |
Prior to
Construction and Construction Phase |
N/A |
||||||||||
Landscape and Visual
(Construction) |
|||||||||||||||||
S.12.9
MM3 |
LV5 |
Open Space Provision - the principles adopted
in the RODP planning ensure that public open space systems are incorporated.
All requirements for open space areas stipulated in the planning documents
for the formulation of the Preliminary Layout Plan should be adhered to. |
Reprovision
of open space. Enhance visual amenity of the area and improve the overall
landscape character |
Government
Developer/ Detailed Design Consultant/ Contractor/ |
Onsite as
stipulated in the planning documents for the formulation of the Preliminary
Layout Plan |
Prior to
Construction and Construction Phas |
N/A |
||||||||||
S.12.9 MM4 |
LV6 |
Tree Protection & Preservation ¡V Exiting
trees to be retained within the Project Site should be carefully protected
during construction. In
particular OVTs will be preserved according to ETWB Technical Circular
(Works) No. 29/2004. Detailed Tree Protection Specification shall be provided
in the Contract Specification. Under this specification, the Contractor shall
be required to submit, for approval, a detailed working method statement for
the protection of trees prior to undertaking any works adjacent to all
retained trees, including trees in Contractor¡¦s works areas. A detailed tree survey will be carried out
for the Tree Removal Application (TRA) process which will be carried out at
the later detailed design stage of the Project. The detailed tree survey will propose
which trees should be retained, transplanted or felled and will include
details of tree protection measures for those trees to be retained |
Protect and
Preserve Trees |
Government
/ Detailed Design Consultant/ Contractor |
Onsite |
Prior to
Construction and Construction Phase |
N/A |
||||||||||
S.12.9 MM5 |
LV7 |
Tree Transplantation ¡V Trees unavoidably
affected by the Project works should be transplanted where practical. Trees
should be transplanted straight to their final receptor site and not held in
a temporary nursery as far as possible. A detailed Tree Transplanting Specification
shall be provided in the Contract Specification, where applicable. Sufficient
time for necessary tree root and crown preparation periods shall be allowed
in the project programme. A detailed transplanting proposal will be
submitted to relevant government departments for approval in accordance with
ETWBTC 2/2004 and 3/2006 and final locations of transplanted trees should be
agreed prior to commencement of the work. For trees associated with highways e.g. roadside planting along highways, that are unavoidably affected and should be transplanted, HyD HQ/GN/13 ¡¥Interim Guidelines for Tree Transplanting Works under Highways Department's Vegetation Maintenance Ambit¡¦ should be referred to. |
Transplant
Trees where suitable for transplantation |
Government
/ Detailed Design Consultant/ Contractor |
Onsite
where possible. Otherwise
consider offsite locations |
Prior to
Construction, Construction Phase & Maintenance in Operation Phase |
N/A |
||||||||||
S.12.9 MM6 |
LV8 |
Slope Landscaping ¡V Site formation should be
reduced as far as possible.
Seeding of modified slopes should be done as soon as grading works are
completed to prevent erosion and subsequent loss of landscape resources and
character. Woodland tree
seedlings and/ or shrubs should be planted where slope gradient and site
conditions allow. In addition, landscape planting should be
provided for the retaining structures associated with modified slopes where
conditions allow. All slope
landscaping works should comply with GEO Publication No. 1/2011-Technical
Guidelines on Landscape Treatment for Slopes. |
To avoid
substantial slope cutting and fill slopes. To prevent
erosion and subsequent loss of landscape resources and character. To ensure
man-made slopes are as visually amenable as possible. |
Government
/ Detailed Design Consultant/ Contractor |
Onsite |
Prior to
Construction, Construction Phase & Maintenance in Operation Phase |
N/A |
||||||||||
S.12.9 MM7 |
LV9 |
Compensatory Planting ¡V Compensatory tree
planting for felled trees shall be provided to the satisfaction of relevant
Government departments. Required
numbers and locations of compensatory trees shall be determined and agreed
separately with Government during the Tree Removal Application process under
ETWBTC 3/2006. Compensatory planting is proposed at the
potential open areas such as open spaces, amenity areas, open areas of the
streetscapes, as well as the open areas within development lots. Compensatory planting for shrubs should be
considered in suitable locations. Native species such as Melastoma malabathricum, Diospyros vaccinioides, Gardenia
jasminoides, Ixora chinensis, Ligustrum sinense, Litsea rotundifolia,
Melastoma dodecandrum, Atalantia buxifolia, Rhodomyrtus tomentosa,
Rhaphiolepis indica, and Rhododendron simsii are suggested. |
Compensate
for trees and shrubs lost due to the Project. |
Government
/ Detailed Design Consultant/ Contractor |
Onsite
where possible. Otherwise
consider offsite locations |
Prior to
Construction, Construction Phase & Maintenance in Operation Phase |
N/A |
||||||||||
S.12.9 MM8 |
LV10 |
Woodland Compensatory Planting ¡VSpecific
Woodland compensatory planting is proposed for any areas of quality woodland
that are unavoidably affected by the Project. The location and design of the
woodland compensatory planting will principally be within habitats of lower
value such as upland grassland. The proposed locations are identified, for
example, on the foothills of Tai Shek Mo, and on the higher ground of Fung
Kong Shan in KTN NDA; along Fanling Bypass; and a small area in the northern
FLN NDA. The intention of the compensatory woodland
will be to recreate areas of quality woodland, not necessarily to compensate
for loss of trees on a like for like basis (See E18 & E27 also). Native tree species are suggested for
planting in the appropriate locations, including Ailanthus fordii, Bischofia javanica, Castanopsis fissa, Celtis
sinensis, Cinnamomum burmannii, Cinnamomum camphora, Xanthoxlyum avicennaeHibiscus
tiliaceus, Liquidambar formosana, Sapium discolor, Schefflera heptaphylla and
Ilex rotunda. In addition some understory vegetation may be planted
including shrubs such as Atalantia
buxifolia, Diospyros vaccinioides, Gardenia jasminoides, Ixora chinensis,
Ligustrum sinense, Litsea rotundifolia, Melastoma malabathricum, Melastoma
dodecandrum, Rhodomyrtus tomentosa, Rhaphiolepis indica, and Rhododendron
simsii. The area allocated for compensatory woodland
planting allows in part for the fact that it will take some time for the
compensatory planting to achieve the landscape and ecological function and
value of the area to be lost. In addition, it allows for the fact that not
all of the areas identified for planting will prove to be plantable, by virtue
of topography and ground conditions and, especially, because though the areas
identified are largely grassland it is inevitable that these areas will
already support some patches of trees and shrubs which would be inappropriate
for further planting. |
|
|
|
|
N/A |
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S.12.9 MM9 |
LV11 |
Vertical Greening ¡V Planting of climbers to
grow up vertical surfaces were appropriate (e.g. building edges, piers). |
Soften hard
surfaces and facilities |
Government
/ Developer/ Detailed Design Consultant/ Contractor |
On
appropriate structures |
Prior to
Construction, Construction Phase & Maintenance in Operation Phase |
N/A |
||||||||||
S.12.9 MM10 |
LV12 |
Green Roof ¡V Roof greening where appropriate
should be established on proposed buildings as per the guidelines stated.
These guidelines provide further details including information regarding
structural loading, design, maintenance, etc. considerations as well as
providing information on what types of plants might be suitable. |
Reduce
exposure to untreated concrete surfaces and particularly mitigate visual
impact to VSRs at high levels. Provide greening. |
Government
/ Developer/ Detailed Design Consultant/ Contractor |
On
appropriate buildings |
Prior to
Construction, Construction Phase & Maintenance in Operation Phase |
N/A |
||||||||||
S.12.9 MM11 |
LV13 |
Screen Planting ¡V Tall
screen/buffer trees and shrubs should be planted. This measure may
additionally form part of the compensatory planting. |
To screen
proposed structures such as roads and buildings. Improve compatibility with the
surrounding environment and create a pleasant pedestrian environment |
Government
/ Detailed Design Consultant/ Contractor |
Along
roads, around suitable built structures, or around VSRs to contain their view
out to the NDA structures. |
Prior to
Construction, Construction Phase & Maintenance in Operation Phase |
N/A |
||||||||||
S.12.9 MM12 |
LV14 |
Road Greening ¡VFor
viaducts, soft landscaping should be provided to soften the hard, straight
edges (for climbers used to cover the vertical, hard surfaces of the piers ¡V
see MM9 Vertical Greening) and shade tolerant plants should be planted, where
light is sufficient, to improve aesthetic value of areas under viaducts. Both
at grade planting and use of elevated planters should be considered for the
soft landscaping of viaducts, taking into account the preference to minimize
the overall viaduct bulk and integrate architectural forms and textural
finishes which improve aesthetics. For at grade roads,
planting should be considered along central dividers and on road islands e.g.
in the middle of roundabouts. (Roadside planting i.e. at the road edge and
not in the central divider or road island, is considered part of Screen
Planting) |
To soften
the hard, straight edges and provide greening along roads. |
Government
/ Developer/ Detailed Design Consultant/ Contractor |
On viaducts
or along roads |
Prior to
Construction, Construction Phase & Maintenance in Operation Phase |
N/A |
||||||||||
S.12.9 MM13
& EIA Annex 13 |
LV15 |
Marsh/Wetland
Compensation ¡VThe proposed Long Valley Nature Park (LVNP) will be designed
and implemented to enhance on- wetland areas within the LVNP. (See E4,E15 and
E25 also) Also see LV16, LV17,
and LV18 as wetland planting should be provided along the embankments and
beds of modified/ reprovisioned watercourses. |
Compensate
for Marsh/ Wetland lost due to the Project. |
Project
Proponent/ Detailed Design Consultant/ Contractor/ Maintenance Authority |
Onsite
where possible. Otherwise consider offsite locations |
Prior to
Construction, Construction Phase & Maintenance in Operation Phase |
N/A |
||||||||||
S.12.9
MM14.1 |
LV16 |
Reprovision of Natural
Stream ¡V Where natural streams are unavoidably affected along some of their
length, they can be diverted to avoid the proposed new developments and
retain the integrity of the whole stream. Detailed design of any stream
diversion should follow the Guidelines in ETWB Technical Circular (Works) No.
5/2005 (Protection of natural streams/rivers from adverse impacts arising
from construction works) and appropriate construction methods should be used. Two short stretches of
the Ma Tso Lung Stream will be affected by Project in the KTN NDA; by the LMC
Eastern Connection Road on the western border of Site F1-3 and further
upstream by Site E-2. At both these
locations, the stream will be reprovisioned and maintain the flow between
unaffected sections of the stream. The reprovisioned stream will be provided
with a natural bed and banks, as well as having an area of marsh/ pool next
to it and trees and shrubs further from the banks. (See E2, E14 and E24 also) |
Achieve a
natural stream, similar to existing, including wetland planting provision for
embankments |
Government
/ Developer/ Detailed Design Consultant/ Contractor |
Streams and
channelized watercourses e.g. a Ma
Tso Lung and Siu Han San Tsuen |
Prior to
Construction, Construction Phase & Maintenance in Operation Phase |
N/A |
||||||||||
S12.9
MM14.2 |
LV17 |
Stream Buffer Planting
¡VProviding a minimum 10 m buffer with planting (where there is a general
presumption against any development taking place) along streams where they
flow close to developments, confers a degree of protection to the stream
course and its associated vegetation. For the stream at Ma
Tso Lung in KTN NDA, the middle and upper sections will be designated as
Green Belt zone where there is a general presumption against development as
buffer to the stream. For the stream at Siu Hang San Tsuen in FLN NDA, within the NDA boundary much of the |