TABLE OF CONTENTS
2.1 Site Location and History of the Project
2.2 Objective and Need of the Project
2.3 Consideration of “With” and “Without” Project Scenarios
2.4 Environmental Benefits of the Project
2.6 Design Changes to the Project
2.7 Consideration of Alignment Options
2.9 Construction Methodologies
2.11 Summary of Alternative Mitigation Measures
2.13 Documentation of Public Concerns
List of Tables
Table 2.1 Summary of Landing Options
Table 2.2 Summary of alignment options
for Tsing Yi Connection
Table 2.3 Summary of alignment options
for Main Bridges cum North Lantau Interchange
Table 2.4 Comparison and Summary of
Possible Construction Methods for the TYLL
Table 2.5 Summary of Key Construction
Works for the Project
Table 2.6 Summary of Alternative
Mitigation Measures
Table 2.7 Summary of Potential
Concurrent Projects
Table 2.8 Summary of the Major
Concerns and the Subsequent Actions Taken in Response
List of Figures
Figures 2.1.1 - 2.1.4 General
Layout Plan
Figures 2.1.5 Alternative
Landing Point Options
Figure 2.2 Proposed
Barging Points for the Project
Figure 2.4 Tsing Yi
Option 2
Figure 2.5 Tsing Yi Option 3 (Recommended)
Figure
2.6 General Arrangement of the Main Bridge –
Main Bridges cum North Lantau Option 1
Figure
2.7 General Arrangement of the Main Bridge –
Main Bridges cum North Lantau Option 2 (Recommended)
Figures
2.8.1 - 2.8.13 Construction Method
Figure 2.9 Alignment
Options for the Tsing Yi Section
Figure 2.10 Tentative
Location for Temporary Concrete Batching Plant
List of
Appendices
Appendix 2.1 Locations of Concurrent Projects
(a) construction
of the cable-supported bridges crossing the MWF and KSMF (hereinafter referred
to as the “Main Bridges”) including:
(i) a
dual three-lane 3-span continuous and earth-anchored suspension bridge crossing
the MWF between Ma Wan and Tsing Yi with a main span of about 1400m;
(ii) a
dual three-lane earth-anchored single-tower suspension bridge crossing the KSMF
between North Lantau and Ma Wan with a main span of about 500m;
(b) construction
of North Lantau Interchange, consisting of slip roads, tunnel and viaducts at
North Lantau to connect the cable-supported bridge crossing the KSMF to North
Lantau Highway, the proposed Tsing Lung Bridge under Route 11 and the proposed
Hong Kong Island West – Northeast Lantau Link (HKIW-NEL Link);
(c) construction
of Tsing Yi Connection, consisting of extension of the TYLL mainline from the
proposed cable-supported bridge crossing the MWF to connect with the Tsing Sha
Highway at the west of Nam Wan Tunnel and provision of slip roads and viaducts
to connect with the local roads in Tsing Yi;
(d) construction
of viaduct at Ma Wan South to connect the cable-supported bridges;
(e) modification
/ realignment of Tsing Sha Highway and Cheung Tsing Highway northbound; and
(f)
associated works including civil, marine, drainage,
sewerage, road works, traffic aids, street lighting, traffic control and
surveillance system (TCSS), toll collection facilities, bridge facilities, fire
services works, electrical and mechanical (E&M) works, re-provisioning of
facilities affected and utility diversion, environmental mitigation works,
landscaping works, site clearance and demolition, earth works, slope works,
geotechnical works, natural terrain hazard mitigation works, reclamation works,
etc.
Table 2.1 Summary
of Landing Options
|
Alignment
Option |
Pros |
Cons |
Recommended
Option (Y/N) |
|
Engineering
Factors |
|||
|
Recommended Alignment |
·
Connection to the Tsing Yi North Coastal Road, Cheung Tsing Highway
and Tsing Sha Highway. ·
Adequate separation between TYLL and Tsing Ma Bridge to prevent
aerodynamic interference. · Smaller reclamation
extent compared to Alternative Landing Options 1 and 2. |
|
Y |
|
Alternative Landing Option 1 |
|
·
No connection to the Tsing Yi North Coastal Road. ·
Travelling distance is about 40% longer than the Recommended Alignment
and may degrade the traffic performance and affect its utilisation, which may
in turn undermine its intended function to divert traffic from other existing
routes such as Tuen Mun Road and the Lantau Link. ·
Additional reclamation works near Tang Lung Chau and Tsing Yi west and
considerable amount of cut slopes and tunneling works associated with the
proposed slip roads in Tsing Yi west would be required, hence resulting in
higher capital and long-term maintenance cost. |
N |
|
Alternative Landing Option 2 |
|
· Aerodynamic
interference of two closely-spaced long-span bridges
would cause road safety concerns on both Tsing Ma Bridge and TYLL. · Additional
reclamation works near Tsing Yi west and realignment of MWF would be
required, hence resulting in higher capital and long-term maintenance cost. |
N |
|
Alternative Landing Option 3 |
|
·
Inadequate space and headroom for proposed slip road connection to
Cheung Tsing Highway and Tsing Sha Highway due to the presence of several
layers of existing viaducts at merging / diverging points. |
N |
|
Environmental
Factors |
|||
|
Recommended Alignment |
·
Smaller reclamation extents when compared with Alternative Landing
Options 1 and 2. ·
Adequate distance maintained between the project and PHIs. |
|
Y |
|
Alternative Landing Option 1 |
|
·
Additional reclamation works near Tang Lung Chau and Tsing Yi west and
considerable amount of cut slopes and tunneling works associated with the
proposed slip roads in Tsing Yi west would be required. ·
Generate large amount of construction
and demolition materials. |
N |
|
Alternative Landing Option 2 |
|
·
Proposed alignment and its associated reclamation would be very close
to the existing residential blocks of Ma Wan and Ma Wan Tung Wan beach,
resulting in significant visual and environmental impacts. |
N |
|
Alternative Landing Option 3 |
|
·
Proposed alignment is close to the existing oil depot and there might
not be adequate space for constructing hazard mitigation measures. |
N |
(a)
Appropriate widening of the marginal strips or hard
shoulders to ensure adequate forward traffic visibility, which would affect the
road design shown in the Tsing Yi Option 1 and require shifting the Cheung
Tsing Highway northbound further west;
(b)
Eliminate the Tsing Yi Road West viaduct by
incorporating it into the Cheung Tsing Highway;
(c)
Provide access for traffic from CTT westbound to TYLL westbound;
(d)
Minimise retaining wall height at Tsing Yi;
(e)
Provide similar connectivity for TYLL and Lantau Link
at Tsing Yi;
(f)
Consider the local geological fault line at Ma Wan;
(g)
Reduce of cut slope extent at TYLL interface with
Route 11 and North Lantau Highway; and
(h)
Provide minimum 270m separation from Tsing Ma Bridge
from the aerodynamic performance viewpoint.
(a)
Tsing Yi Connection; and
(b)
Main Bridges cum North Lantau Interchange.
Table 2.2 Summary
of alignment options for Tsing Yi Connection
|
Alignment
Option |
Pros |
Cons |
Recommended
Option (Y/N) |
|
Engineering
Factors |
|||
|
Tsing Yi Option 1 |
·
Direct connection to Tsing Yi Road West. |
· TYRW-TYLL
Viaduct requires land adjacent to Sai Tso Wan Road. · No
direct connection between TYLL and CTT. ·
Large temporary working platforms are anticipated
for the construction of bored pile wall along existing slopes. |
N |
|
Tsing Yi Option 2 |
· The
amount of retaining structures is less than the Tsing Yi Option 1. |
· TYRW-TYLL
Viaduct requires land adjacent to Sai Tso Wan Road. · Appropriate
widening of the marginal strips or hard shoulders to satisfy adequate forward
visibility distance. ·
No direct connection between TYLL and CTT. |
N |
|
Tsing Yi Option 3 (Recommended) |
· The
amount of retaining structures is fewer than the Tsing Yi Option 1 and 2. · The
modification of existing road is less than Tsing Yi Option 2 by approximately 4.3km. · Direct
connection of TYLL westbound and CTT westbound. · TYRW-TYLL
Viaduct incorporated into Tsing Sha Highway. |
· Appropriate
widening of the marginal strips or hard shoulders to satisfy adequate forward
visibility distance. · Large
temporary working platforms are anticipated for the construction of bored
pile wall along existing slopes. |
Y |
|
Environmental
Factors |
|||
|
Tsing Yi Option 1 |
|
· Affect
large number of trees (~909 nos. of trees) at
existing slope. · Closer
to the two existing PHIs (~20m) and ASRs at Sai Tso Wan. ·
Large construction area
would impose greater environmental implication. |
N |
|
Tsing Yi Option 2 |
|
· Affect
large number of trees (~909 nos. of trees) at
existing slope. · Closer
to the two existing PHIs (~10m) and ASRs at Sai Tso Wan. · Large construction area would impose greater environmental
implication and generate higher amount of construction waste. |
N |
|
Tsing Yi Option 3 (Recommended) |
· Omission
of viaduct connection leads to smaller construction works area and minimise
landscape and visual impacts. · Affect smaller number of trees (~461 nos. of
trees) at existing slope. · The
works area is reduced by 15 ha as compare
with Tsing Yi Option 1 and 2 |
|
Y |
Table 2.3 Summary of alignment
options for Main Bridges cum North Lantau Interchange
|
Alignment
Option |
Pros |
Cons |
Recommended
Option (Y/N) |
|
|
Engineering
Factors |
||||
|
Main Bridges cum North Lantau Option 1 |
·
Full closure to KSMF is not required for cable-stayed bridge
construction. |
·
KSMF cable-stayed bridge does not comply with Disneyland Height Restrictions. ·
Reduces the airspace at North Lantau Interchange for helicopter
flights. ·
Increased deck width of Lantau side span is required to cater for the
merging/diverging length. ·
Significant increase in site formation and tunnelling works required
on North Lantau Island. |
N |
|
|
Main Bridges cum North Lantau Option 2 (Recommended) |
· Complies
with Disneyland Height Restrictions. · Curved
alignment begins at Lantau Shoreline with reduced site formation works. |
· One-off
short duration of full closure at KSMF is required. |
Y |
|
|
Environmental
Factors |
||||
|
Main Bridges cum North Lantau Option 1 |
|
·
Require reclamation at North Lantau and larger reclamation area in Ma
Wan. The total reclamation area is
approximately 26.3 ha. ·
Generate large amount of marine sediment due to larger reclamation
area. ·
Affect larger number of trees (2,420 nos. of trees). |
N |
|
|
Main Bridges cum North Lantau Option 2 (Recommended) |
· Reclamation
at North Lantau is not required. · The total
reclamation
area is approximately 19.8ha.
Reduced the overall area of reclamation by approximately
6.5 ha as compared with Main Bridges cum North Lantau Option 1. · Minimise
slope cutting at North Lantau which in turn preserves the natural features of
the area hence minimising ecological impacts and tree felling. · Affect smaller number of trees (1,920 nos. of
trees). |
|
Y |
|
(a)
Additional reclamation, site formation, slope cutting
and tunnel works are avoided, resulting in cost saving with less generation of
C&D materials, less environmental impacts and less impact to the natural terrain;
(b)
Encroachment of bridge towers into MWF is avoided,
hence less impact to marine traffic;
(c)
Aerodynamic interference between the existing Lantau
Link and the proposed TYLL, which results if the long span bridges are located
close to each other, is avoided; and
(d)
The provision of connection to Tsing Yi North Coastal
Road, and shorter travelling distance, render better traffic performance.
(a) Tsing
Yi Option 1 does not allow the traffic from CTT westbound to TYLL
westbound. A slip road connecting Cheung
Tsing Highway northbound and TYLL westbound is therefore proposed to facilitate
the westbound traffic of CTT to have a direct access to TYLL westbound and thus
better connectivity with CTT; and
(b)
With the provision of the slip road mentioned above,
both bound traffic between TYLL and the existing local road, i.e. Tsing Yi Road
West, can be maintained and the pair of slip roads running along Sai Tso Wan
Road proposed in the Tsing Yi Option 2 is no longer required. The enhanced Tsing Yi Connection under the
Recommended Alignment will be more cost-effective land impact is also
minimised.
(a)
On the western side of the single-tower suspension
bridge, the prismatic cable-supported portion of the bridge deck will terminate
at the approach to Lantau shoreline and allow the alignment of TYLL mainline to
turn northeast earlier towards Route 11 and thus can greatly minimise the
extent of site formation and slope cutting works for the construction of the
proposed North Lantau Interchange, resulting in cost saving with less
generation of C&D materials, less environmental impacts and less impact to
the natural terrain;
(b)
Owing to the termination of the bridge deck of
single-tower suspension bridge at the Lantau shoreline mentioned above, this
will not impose constraints on the design of the proposed North Lantau
Interchange and the connection with the slip roads of the interfacing projects;
(c)
The common marine anchorage for both suspension
bridges near the south-eastern corner of Ma Wan Island is modified. There will be a section of about 200 m long
free of suspenders in between the two suspension bridges. This section will be in the form of concrete
viaducts, resulting in cost saving with a shorter length of the side span of
the single-tower suspension bridge at the south of Ma Wan;
(d)
Taking into
account the bridge form for crossing the KSMF and the
modified layout of North Lantau Interchange, the alignment option with
single-tower suspension bridge form will have a noticeable lower overall
construction cost;
(e)
The airspace in the vicinity of the KSMF will continue
to be free in absence of a bridge tower on Lantau side and thus no interference
with the existing helicopter flight path; and
(f)
Single-tower suspension bridge will only have one
bridge tower located at the south of Ma Wan hence complying the Disneyland
Height Restrictions.
1. Installation of silt curtain;
2. Dredging for seawall and four main reclamation
areas simultaneously (Approx.12 numbers of dredgers);
3. Installation of geotextile, sand blanket and
primary silt curtain;
4. Carry out DCM (approx. 50%) for main reclamation area;
5. Backfilling of fully dredged zone;
6. Installation of rockfill; and
7. Reclamation filling to formation level.
·
In order to preserve the headwater of
the north-branching tributary in watercourse at North Lantau, it is proposed to
replace the intersecting section with a box culvert and relocating the
permanent structures to avoid encroachment;
·
Implement temporary stream
diversions to maintain waterflow and minimise run-off
as well as subsequent impact on watercourses and associated fauna; and
· Establish work exclusion zones around watercourses
and use elevated platforms to minimise impact on banks and stream beds.
Table 2.4 Comparison and
Summary of Possible Construction Methods for the TYLL
|
Section |
Possible
Construction Method |
Pros |
Cons |
|
Tunnel |
Drill-and-blast (Recommended) |
· Significantly decrease and limit potential
environmental impacts, specifically concerning noise, dust, and visual
disturbances to areas in close proximity to the
portals · More
effective for rock tunnel excavation than mechanical breaking methods,
which significantly reduces the construction period, providing both financial
benefits and a faster project commissioning |
· Risk of storage and delivery of explosives to
work site. |
|
Tunnel Boring Machine |
· Less labour required for the construction of
tunnel. |
· Less suitable for hard ground profiles such a
those found in North Lantau. · Land required for set of launching shaft and receiving shaft
which would impose significant impact on natural terrain causing
consequential ecological impact. |
|
|
Reclamation |
DCM (Recommended primary ground treatment method) |
· Considered as the most robust option with the
least shortcomings when compared with other ground treatment schemes given
the Project’s needs. · Avoid the need for disposal of thick marine
deposits. |
· Ineffective in areas with shallow depth of marine
deposits. |
|
Fully dredged method (Recommended for areas where
DCM is ineffective) |
· For areas with soft marine deposits where DCM is
ineffective, it is technically required to dredge the whole layer of marine
deposits and replace it with firm materials for controlling the settlement of
the reclaimed islands and to ensure stability of the seawall structures |
·
Disturbance of seabed may cause generation of
suspended solids. |
|
|
Pile-supported VIPS |
Bored pile (Recommended) |
·
The bored piles would be used for supporting the
VIPS. It aims to provide the protection to bridge structures. ·
Reduction in vibration
and noise generated during the piling process |
· More expensive |
|
Driven pile |
· Less expensive |
· Generation of significant noise and vibration
during the piling process. · Percussion piling may cause disturbance to the
seabed and generate suspended solids. |
|
|
Main Bridges- foundations |
Large diameter bored pile foundations for tower
support (Recommended) |
· Accelerate
construction · Reduce
noise and minimising vibrations |
·
More expensive |
|
Driven pile |
·
Less expensive |
· Generation of significant noise and vibration
during the piling process. · Percussion piling may cause disturbance to the
seabed and generate suspended solids. · Driven piles may not have enough capacity for the
large loads from the towers |
|
|
Main Bridges- tower |
Jump form or slip form methods for tower
construction (Recommended) |
·
Considered as the most
robust option taking account into the construction time, cost, durability,
and maintenance requirements. ·
Less C&D materials / waste generated |
· Require another trade of skilled workers and
additional construction equipment. |
|
Timber formwork for tower construction |
· Conventional construction method and require less
special skilled labour force and specialists when comparing with other
construction methods |
· More
C&D materials / waste to be generated |
|
|
Viaducts |
Precast concrete segmental method (Recommended) |
· Better control of quality and workmanship for
works in fabrication yard. · Minimise the need for on-site concrete casting. · Use of steel mould as formwork in the fabrication
yard can reduce the generation of C&D waste / materials on site. · More efficient construction works as the deck
segments can be casted concurrently with superstructure works. |
· Require another trade of skilled workers and
additional construction equipment for erecting precast segments. |
|
Cast in-situ concrete |
· Conventional construction method and require less
special skilled labour force and specialists when comparing with other
construction methods |
· Use of timber formwork, thus more C&D waste /
materials will be generated. · Site conditions in terms of accessibility and
weather can be highly critical to the work, requirement of extreme measures
in some situations to control all stages in the production process. · Substantial falsework required. · Longer construction time. |
|
|
Rock Cuttings |
Open blasting (Recommended for Lantau side) |
· Optimise
cost and time efficiency for hard rock slopes. · Noise only
generated at specific times. |
·
Risk of storage and delivery
of explosives to work site. |
|
Hydraulic excavation (Recommended for Tsing Yi
side) |
·
Explosives not required, thus reducing risk to the
two PHIs at Tsing Yi. |
·
Longer periods of continuous noise generation. ·
Longer construction time |
·
Close liaison with the
contractors of other concurrent projects in order to
avoid overlapping of construction activities and allow sufficient buffer for
works at project interface due to potential delays in the programme so that the
cumulative effects of environmental impacts could be minimised.
Land Based Works
·
Temporary stream diversion
to maintain the downstream water flow, works exclusion zones and elevated
platforms will also be implemented before construction works around
watercourses where required to minimise the ecological impact. As the impact on
amphibians and other aquatic species of conservation interest are mitigated
through translocation works (if applicable) after pre-construction survey, the
environmental impact has been minimised such that a specific sequence of
land-based works is not considered necessary.
·
Blast cages or roof-over protective cover would be provided before the
commencement of open blasting works to minimise the air and noise impacts of
blasting. During the construction of drill and blast tunnels, a blast door will
be installed in the tunnel openings to prevent the escape of fugitive dust from
blasting before further blasting works within the tunnels. Therefore, the air
and noise impacts are minimised for most periods of the tunnel construction
through the blast door. With these mitigation measures, the carrying out of the
construction of the two tunnels and slip roads concurrently would result in a
similar environmental impact and is assumed in conducting the assessment in
lieu of a specific construction sequence.
Marine Works
·
Silt curtains will be
installed before reclamation works to minimise the marine water quality, marine ecology and fisheries impacts of the
works. The worst-case scenario has been
considered for the water quality impacts of the reclamation works in Chapter
5 based on a tentative construction sequence in Appendix 5.2.
·
The use of VIPS for vessel
protection of the deflection pier at North Lantau reduces the time required for
the construction works there when compared to using reclamation for vessel
protection, requiring only about 10 months to complete the piling works. This
further minimises the marine water quality, marine ecology and fisheries
impacts of the works. The sediment release rate for VIPS is minuscule,
being less than 1% of the sediment release rate of the reclamation works.
Therefore, it is considered that a specific sequence of works for VIPS is not
necessary.
Table 2.5 Summary
of Key Construction Works for the Project
|
Description |
Tentative Construction Programme |
|
Tsing Yi Connection |
Q1
2027 to Q2 2031 |
|
Suspension bridge over Ma Wan Fairway |
Q1
2027 to Q2 2033 |
|
Viaduct connecting two cable-supported bridges |
Q1
2028 to Q4 2031 |
|
Suspension bridge over Kap Shui Mun Fairway |
Q1
2027 to Q2 2030 |
|
North Lantau Interchange |
Q1
2027 to Q2 2031 |
|
Alternative Mitigation Measures |
Details |
Environmental Benefits |
Environmental / Engineering Disbenefits |
|
Reduce and reuse inert C&D Materials |
·
Minimise
slope works in North Lantau and Tsing Yi to reduce generation of excavated
soil and yard waste; and ·
On-site
reuse of inert C&D materials like reclamation filling. |
·
Reduce
total amount of inert C&D materials for disposal; and ·
Minimise
transporting of C&D materials to Public Fill Reception Facilities (PFRFs)
thus reducing potential air quality and noise impacts arising from the
transportation vehicles / vessels. |
·
NIL |
|
Encourage recycling of yard waste |
·
Yard
waste is encouraged to be sent to the Yard Waste Recycling Centre in Y-Park
for recycling prior to disposal at the designated landfill site. |
·
Generate
new products from yard waste; and ·
Indirectly
increasing the lifespan of existing landfill. |
·
Yard
waste might need to be stored on-site for a period; and ·
Increase
in administration cost. |
|
Adopting GPS or equivalent system |
·
Tracking and monitoring of all dump trucks to prohibit illegal dumping
and landfilling of C&D materials. |
·
Prohibit illegal dumping. |
·
NIL |
|
Disposal / treatment methods for marine sediment |
·
Adoption
of DCM as a primary ground treatment method for reclamation. |
·
Avoid
the need for disposal of thick marine deposits; and ·
Reduce
disposal and transportation of marine sediment. |
·
Ineffective
in areas with shallow depth of marine deposits; ·
May
involve specialised equipment, materials, and expertise, leading to higher
upfront costs compared to traditional dredging |
|
Adopt
pile-supported VIPS in
the area of existing shoreline. |
·
Avoidance
of reclamation at North Lantau shoreline; and ·
Protect
the deflection pier at North Lantau from vessel impact. |
·
Reclamation is no longer
required at North Lantau, which benefit the preservation of the intertidal
zone and ecosystem along the shoreline; and ·
Alleviate
the water pollution caused by the construction of reclamation land. |
·
The
VIPS and other pile-supported structures require ongoing maintenance to ensure
their structural integrity, especially in a harsh marine environment. |
|
Adoption of Eco-shoreline |
·
Incorporation
of eco-shoreline design in the future coastal structures such as seawalls on
the reclaimed land as well as surfaces and supporting structures on the
pile-supported VIPS; and ·
Incorporation
of elements that diversify microhabitats and enhance the quality of
settlement substrates. |
·
Present
new opportunities for the recruitment, settlement and colonisation of marine
benthos, thereby enhancing the overall quality of associated marine
ecosystems in the vicinity; ·
Encourage
recruitment and settlement of corals and other benthos; and ·
Provide
sheltering habitats for marine wildlife. |
·
Increase
in construction cost and maintenance cost. |
|
Concurrent Project |
Description |
Tentative Programme |
Assessment of Potential Cumulative
Environmental Impact |
|||
|
Start |
Complete |
Reference for Programme |
Construction Phase |
Operation Phase |
||
|
Hong
Kong Island West – Northeast Lantau Link (HKIW-NEL
Link) |
The road
project comprises land and subsea tunnels, land and marine viaducts, and
at-grade roads. |
Under Planning [1] |
Under Planning [1] |
Project
Profile of the Concurrent Project [PP-635/2021] |
Cumulative
impacts were evaluated in this EIA report. |
Cumulative
impacts were evaluated in this EIA report. |
|
Road
P1 (Tai Ho- Sunny Bay Section) |
The
road project comprises land viaducts and tunnels, reclamation, and at-grade
road. |
2027 |
2031 |
Project
Profile of the Concurrent Project [PP-615/2020] |
Cumulative
impacts were evaluated in this EIA report. |
Cumulative
impacts were evaluated in this EIA report. |
|
Route
11 (section between Yuen Long and North Lantau) |
Highway
project connecting Yuen Long and North Lantau. |
2026 |
2033 |
EIA
Report of the Concurrent Project [AEIAR-255/2023] |
Cumulative
impacts were evaluated in this EIA report. |
Cumulative
impacts were evaluated in this EIA report. |
|
Underground
quarrying contract at Tsing Yi North |
An
underground quarry in the form of cavern and access tunnel with ancillary
operations |
2027 |
2028 |
N/A |
Cumulative
impacts were evaluated qualitatively in this EIA report. |
Details
of the development (including its emission sources) are not available during
the preparation of this EIA study. On
this basis, the cumulative impact from the project (if any) would be
considered in separate studies of the project by the respective project
proponent. |
|
Sunny
Bay Development |
Establish
the reclamation and infrastructure works extent for
future land use. |
To
be confirmed. (Note: As this project is under review, there is no concrete
implementation schedule / construction programme.) |
Cumulative
impacts were evaluated qualitatively in this EIA report. |
No concrete implementation
programme nor approved rezoning proposal / planning application is available
during the preparation of this EIA study.
On this basis, the cumulative impact from the project (if any) would
be considered in separate studies of the project by the respective project
proponent. |
||
|
Private
Housing Development in Ma Wan South |
Housing
development |
To
be confirmed. (Note: No
concrete implementation programme nor approved rezoning proposal /
planning application is available during the preparation of this EIA study.) |
Cumulative
impacts were evaluated qualitatively in this EIA report. |
Cumulative
impacts were evaluated qualitatively in this EIA report. |
||
|
Hongkong
United Dockyards (HUD) Development |
Housing
development |
To
be confirmed. (Note: No
concrete implementation programme nor approved rezoning proposal /
planning application is available during the preparation of this EIA study.) |
Cumulative
impacts were evaluated qualitatively in this EIA report. |
Cumulative
impacts were evaluated qualitatively in this EIA report. |
||
Notes:
[1] While
the pace to take forward the HKIW-NEL Link had slowed down and the commencement
of works would be further reviewed; the relevant road networks have been
included in this EIA study for the sake of evaluating the cumulative impacts.
|
Key Concerns / Issues |
Follow Up Actions Taken |
|
Alignment, Footprint, Reclamation and Associated
Facilities |
|
|
Minimise the project footprint, including but not
limited to the road corridor and slope works. |
· The
Project's at-grade footprint has been minimised by adopting tunnel design for
slip roads to avoid at-grade works near Tai Chuen in North Lantau. ·
Due considerations have been taken to minimise slope
works in North Lantau and Tsing Yi. |
|
Minimise the extent of reclamation while ensuring
the incorporation of necessary eco-features. |
· The
reclamation area at Ma Wan has been reduced by adopting a shared marine
anchorage at Ma Wan. ·
No reclamation area at North Lantau is required due
to the shifting of the deflection pier inland and adopting VIPS as bridge protection measures. ·
Eco-features would be
adopted at the shoreline where
possible. |
|
Concurrent
Projects and Cumulative Impacts |
|
|
HUD development and Ma Wan South Development (MWSD)
have not been included as sensitive receivers |
·
The rezoning application
for the HUD development is still on-going and has not been approved, while
the rezoning proposal for the MWSD has not yet commenced. There is no solid
information on the implementation programme and approved associated design
plan available for these projects. ·
Hence, these two projects
are not considered as planned sensitive receivers. ·
Cumulative impacts from these
projects have been considered qualitatively in the EIA report. |
|
Air Quality |
|
|
The project must comply
with Air Quality Objectives (AQOs) at sensitive receivers to ensure
acceptable air quality levels. |
·
The Project will comply
with the Air Quality Objectives (AQOs) at all air sensitive receivers within
the assessment area. |
|
Cumulative air quality
impacts of the western territory (including Yuen Long, Tuen Mun, Tung Chung,
Kwai Chung, Tsuen Wan, Centra/Western) shall be assessed. |
·
Cumulative air quality
impact from concurrent projects has been assessed in accordance with the EIA
Study Brief. The concerned areas
mentioned are however outside the 500m assessment area. |
|
The construction vehicles
associated with the proposed Project should not be allowed to access to
Lantau Island except the delineated works area directly required by the
Project. |
·
During construction, the
haul roads should be paved and regularly wetted to suppress the fugitive dust
emission. Vehicles transporting dusty
spoil would be properly covered with mechanical covers or tarpaulin sheets to
avoid any dust pickup by gust during travel. ·
Construction vehicles will follow designated
transportation routing to avoid use of any local
roads, and the truck traffic should avoid peak hours, as far as practicable.
Dump trucks are equipped with water-tight container
and mechanical cover, which would not cause fugitive
dust emission on the open road. With the implementation of these design
measures, it is anticipated that no adverse air quality impact would be
caused by the transportation of spoils along the routes. |
|
Noise |
|
|
The noise criteria specified in the Technical Memorandum on
Environmental Impact Assessment at sensitive receiver locations shall be
complied with. |
·
Noise criteria at all
noise-sensitive receivers within the assessment area will be fulfilled. |
|
Cumulative noise impacts shall be assessed. |
·
Cumulative noise impacts from concurrent
projects have been assessed in accordance with the EIA study brief. |
|
Illegal Dumping |
|
|
Effective measures to
control the illegal dumping of Construction and Demolition (C&D)
materials shall be applied. |
·
All dump trucks should
adopt GPS or equivalent system for tracking and monitoring of the travel
routings to prohibit illegal dumping and landfilling of C&D materials. |
|
Ecology and Fisheries |
|
|
The ecological importance of North Lantau should be taken into account. |
· Through
careful optimisation of the Project's footprint and adoption of tunnel and
viaduct sections, the permanent loss of natural shrubland and grassland and
the areas south of North Lantau Highway has been minimised. · Minimisation
and optimisation of at-grade works, with tunnels and viaducts designed
adopted, where feasible, especially at Yi Chuen, to reduce watercourse loss
in W2 and W3. · Headwater
preservation in W2 and replacing intersecting section with box culvert to
retain waterflow will be implemented to reduce indirect impact on Romer’s
Tree Frog. · Adoption
of viaduct sections and adjustment of tunnel portal location at North Lantau
to avoid direct encroachment on watercourse W3 that houses Caridina serrata,
thereby reducing any potential impacts on this species. · The
Project has taken measures to avoid any direct impact on fauna species of
conservation importance, such as the Romer's Tree Frog. |
|
Impacts on Chinese White Dolphins (CWD), Brothers
Marine Park and mariculture zones should be adequately assessed. |
·
The project site is not a key habitat of CWD. The
ecological impact assessment has covered an area of 500m as well as other
areas likely to be impacted by which included Brothers Marine Park (which is
located approx. 4km from the project site). · Fisheries
impact assessment has been conducted according to the requirements of the
EIA-SB. Ma Wan FCZ is the only fisheries sensitive receiver in the vicinity
of the project which is located about 450m away from the project area. No WQ
exceedance expected with deployment of silt curtains. |
|
Landscape
and Visual |
|
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To adopt adequate landscape and visual mitigation
measures. |
·
As stated in above, reclamation extent and slope
extent are avoided or minimised subject to engineering design. · Landscape
works are proposed at the reclamation area and affected slope features. · Aesthetical
design on main bridges and viaducts to blend in with the surrounding
environment. |