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Ove Arup & Partners
Hong Kong Ltd 80 Tat Chee Avenue Kowloon Tong Kowloon Hong Kong |
13.1
Population and Environmental Areas
Protected
Affected Population along the Project
13.1.1 According to the RODP, the estimated total
number of resident for the development is 25,000. The total area of the
platform area for the development is approximately 40ha. The average plot ratio
for subsidised housing and private housing is 6.3 and 4.2 respectively.
13.1.2 The construction/ development of the Study
Area will commence after the rehabilitation contract (No. GE/96/10) has been
completed and the site handed over to the Project Proponent. Hence, no land
resumption is required for the development.
13.1.3 To minimise the potential environmental
nuisance during the construction phase, phasing of the construction programme
is proposed. In addition, good site practices and mitigation measures have been
recommended in this study to ensure compliance of the relevant legislation/
standards during the construction and operational phase of the Project.
Habitat Compensation
13.2
Environmental Friendly Design and Benefits
13.2.1 Key green features incorporated into the
Urban Design Plan of the ARQ development (refer Appendix 13.1) is summarised below.
Pedestrian Corridors
13.2.2 Three pedestrian corridors will be provided.
The first corridor runs north-south parallel to the rock face
through the Northern Community, linking the residential area to the Quarry
Park at one end and the Civic Core at the other. It is also proposed with a
cycling path to connect private housing sites to the Civic Core. The second
corridor links the District Open Space in DAR to the rock face through the
Civic Core and serves as a major pedestrian connection between the Planning
Scheme Area and its surrounding. The third corridor runs
north-south connecting all residential and school sites in the Southern Community,
and a 10m-wide green corridor will be reserved to enhance the pedestrian
environment. It will also provide a legible path for keen walkers who want to
access from Po Lam Road to key destinations within the ARQ.
13.2.3 A pleasant environment along the Pedestrian
Corridors will be created by providing enhanced streetscape design and
treatments of site frontages along the corridors. The Pedestrian Corridors will
be well-lit and be made fully accessible with ramps or elevators if
necessary. A cover for the walkway will be considered especially at locations
where two public buildings can easily be connected or people are likely to
congregate. Directional signs for key designations should also be provided at
regular intervals.
Open Space and Landscape Framework
13.2.4 A Quarry Park has been
proposed all along to the southwestern boundary and northwestern portion (refer Appendix 13.1). The
southern portion of the Quarry Park will be a Green Promenade along the
platform edge adjoining DAR. It will provide a relaxing open space for
the future residents of the ARQ,
DAR and the wider Sau Mau Ping area.
13.2.5 The open space network will extend from the
Quarry Park and weave into the residential areas. Green Spines and
Pedestrian Corridors will not only serve as interior linkages to the site
development, but will become linear open spaces with ample space for pedestrian,
circulation network and greenery. They will be designed with the
provision of seating, urban hard landscape features and visual landscape
amenities for visual relief.
Building Height Strategy and View Corridor
13.2.6 Building height restrictions have been
imposed to protect the visual access to Tai
Sheung Tok ridgeline from territorial vantage points at Hong Kong
Island north or future Kai Tak development area. Further building height
limits have been imposed on residential developments along major public
spaces and pedestrian corridors to create a more open and humanistic
living environment, and a visually interesting
development profile that complements the dramatic rock face and
ridgeline of Tai Sheung Tok.
13.2.7 Low-rise residential blocks ranging from 30m
to 40m will be provided fronting the Quarry Park and the Green
Promenade to create a more humanistic-scale environment along major
public realms and introduce height variations to the building cluster.
High-rise residential blocks ranging from 80m to 100m will be restricted to the
sites closest to the rock face backdrop to minimize the possible adverse
visual impacts of the blocks. Medium-rise blocks ranging from 50m to 75m
will be built in between the low-rise and high-rise blocks to create
stepped height profiles.
13.2.8
Generous visual corridors have been
preserved between building clusters in order to secure inter-visibility between the
Sau Mau Ping area and the rock face. They also serve as visual relief
within the new development. In particular, a low-rise building zone is
designated at the civic core to preserve an
unobstructed view for visitors on the lookout on the rock face and to
create a generous visual relief for the Sau Mau Ping area.
13.3
Summary of the Measures taken for the
Avoidance and Minimisation of Environmental Impacts
13.3.1 The various chapters of this EIA Report
have presented key measures to minimise the potential environmental impacts
associated with the Project in the construction and operational stages. Key measures
to minimise the environmental impacts are summarised as below:
Phasing of Implementation
13.3.2
In order to minimise the environmental
nuisance during the construction phase, the Project will be implemented in
phases. Table 13.1 summarises the
phasing of the implementation.
Table
13.1: Summary of the
tentative implementation programme
Works Package |
Works Components |
Time Line |
Works Package 1 |
Site formation at the southern portion of the Study Area |
mid 2016 – end 2018 |
Internal roads at the southern portion of the Study Area |
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Access road for main external access via. Po Lam Road |
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Access road for supplementary external access via. DAR local road with associated bus bays and semi-enclosure noise barrier |
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Supporting infrastructure works, including two-way escalators and subways, for pedestrian connectivity between development of ARQ and DAR |
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Stormwater drainage systems at the southern portion of the Study Area |
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Sewerage systems at the southern portion of the Study Area |
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Water supply systems at the southern portion of the Study Area |
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Landscaping at the southern portion of the Study Area |
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Works Package 2 |
Site formation at the northern portion of the Study Area |
early 2018 – end 2020 |
Internal roads with associated public transport terminus at the northern portion of the Study Area | ||
Stormwater drainage systems at the northern portion of the Study Area | ||
Sewerage systems at the northern portion of the Study Area | ||
Water supply systems at the northern portion of the Study Area | ||
Landscaping at the northern portion of the Study Area | ||
Works Package 3 | Drainage retention tanks in the Study Area | mid 2016 – mid 2019 |
Works Package 4 | Viewing platforms | early 2018 – end 2020 |
Works Package 5 | Salt and fresh water pumping stations in the Study Area | mid 2018 – end 2020 |
Service reservoirs in the Study Area | ||
Works Package 6 | Road improvement works at J/O Lin Tak Road and Sau Mau Ping Road, including road widening works at Lin Tak Road and a new vehicular bridge form Link Tak Road to Sau Mau Ping Road with associated semi-enclosure noise barrier |
early 2017 – early 2022 |
BBI at TKO Tunnel Toll Plaza Area | ||
Pedestrian crossing facilities, including footbridge with lift towers and subway | ||
Associated site formation works | ||
Works Package 7 | Road improvement works at J/O Clear Water Bay Road and Road L1 constructed under DAR, including provision of u-turn facility. |
early 2017 – early 2021 |
Road improvement works at merging lane at New Clear Water Bay Road near Shun Lee Tsuen Road, including increase of merging length | ||
Associated site formation works | ||
Works Package 8 | Rock cavern development |
early 2018 – end 2020 |
Construction Dust
13.3.3 In order to reduce the dust impact and
achieve compliances of TSP criteria at the ASRs, watering once per hour on the
exposed worksites and haul road is recommended. In addition, the dust control
requirements stipulated in the Air Pollution Control (Construction Dust)
Regulation and good site practices would be in place to further minimise the
potential construction dust impact. These would include:
(1) 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;
(2) Any dusty material remaining after a stockpile is removed should be wetted with water and cleared from the surface of roads;
(3) A stockpile of dusty material should not extend beyond the pedestrian barriers, fencing or traffic cones;;
(4) The load of dusty materials on a vehicles leaving a construction site should be covered entirely by impervious sheeting to ensure that the dusty materials do not leak form the vehicle;
(5) Where practicable, vehicles washing facilities including a 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; and
(6) 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.
Construction Noise
13.3.4 The following mitigation measures have
been considered to tackle the construction noise impact:
(1) Good site practices to limit noise emissions at the source;
(2) Use of quiet plant and working methods;
(3) Use of site hoarding as noise barrier to screen noise at ground level of NSRs;
(4) Use of shrouds / temporary noise barriers to screen noise from relatively static PMEs;
(5) Use of large full enclosure to screen all the plant, wherever practicable;
(6) Scheduling of construction works outside school examination periods in critical area; and
(7) Alternative use of plant items within one worksite, wherever practicable.
Fixed Noise and Road Traffic Noise
13.3.5 Maximum allowable sound power levels (SWL)
have been specified for the proposed pumping station for saltwater and
freshwater and the planned rock cavern developments. Detailed design of the
proposed pumping station (e.g. the louver details) are yet to be developed,
nevertheless, it is recommended that the detailed design should incorporate
good practices such as orient louvres away from adjacent NSRs, use of direct
noise mitigation measures e.g. silencers, in order to minimise the nuisance on
the neighbouring NSRs. Operational road traffic noise impact on the sensitive
uses along the Road L4 outside the Study Area would be mitigated by the
provision of direct mitigation measure in
the form of semi-enclosure.
Water Quality
13.3.6 To minimise water quality impacts during
the construction phase, best management practices in accordance with the
Practice Note for Professional Persons on Construction Site Drainage,
Environmental Protection Department, 1994 (ProPECC PN 1/94) should be
implemented as far as practicable.
Sewerage and Sewage
13.3.7 After incorporated latest planning information with total 25,000 and
48,600 populations from ARQ and DAR developments in the hydraulic model
network, the discharge peak flow from East Kowloon catchment to KTPTW has been
evaluated as 10.93m3/s.
13.3.8 Based on the latest
available development parameters for the on-going
projects, the total discharge peak flow to KTPTW will be 12.82m3/s. It shows that KTPTW with 10.92m3/s capacity is inadequate to cater for the predicted
peak flow. It is understood that EPD’s “Upgrading of Kwun Tong Preliminary
Treatment Works – Feasibility Study, Agreement No. CE5/2008(DS)” recommended to
upgrade the peak capacity to 13.14m3/s and should be adequate.
The anticipated completion date of the KTPTW upgrading works is June 2021,
whilst the first population intake of the ARQ is planned in 2022, hence no
programme gap is anticipated between the completion of the KTPTW upgrading
works and the ARQ development.
13.3.9 Two routes are proposed in
ARQ sewerage system (total
2.8km long from size 300mm to
450mm diameter) to collect the sewage generated from ARQ development and convey to
downstream sewerage system. Improvement recommendations have been drawn for the
surcharged sewers with less than 1 metre freeboard caused by ARQ development. 400m of the downstream sewers at Po Lam Road are recommended to be upgraded from size 225mm to 450mm diameter. In addition, no other further
downstream sewers are proposed to be upgraded.
Waste Management
13.3.10 The amount of C&D material that would
need to be transported off site has been minimised as far as practicable in the
implementation programme. Opportunity for re-using C&D material has been
fully considered and implemented where practicable. Good site practices have
been recommended for chemical waste, general refuse and disposal of chemical
waste will follow the relevant ordinances.
Land Contamination
13.3.11 A total of five potentially contaminated
areas located on fill material in the Study Area were proposed for
environmental SI. However, as all areas proposed for environmental SI are
privately owned and still in operation, undertaking the environmental SI works
at this EIA stage is not feasible. The proposed environmental SI works for
these areas should commence once the operation is terminated and the land is
resumed.
13.3.12 Following the completion of the
environmental SI works, a CAR to present the findings and evaluate the level
and extent of potential contamination. If land contamination is identified and
remediation is required, a RAP will be prepared to recommend specific
remediation measures. Upon completion of the remediation works, if any, a RR
that demonstrates the clean-up works are adequate would also be prepared. CAR,
RAP and RR would be submitted to EPD for approval prior to commencement of any
construction / development works.
Ecological Impact
13.3.13 Measures recommended to avoid, minimise and compensate for the potential ecological impacts of the Project are summarised below:
Measures to compensate
the woodland habitat loss
13.3.14 A combined area of 1.13 ha young secondary woodlands will be directly
impacted by the proposed road and underpass at the southeast of the Study Area.
Loss of this habitat is compensated by planting of native tree and shrub
species at the proposed Wooded Area (about 1.2 ha). This Wooded Area is located
within the proposed Quarry Park at the northern side of the ARQ, and connected
to the existing benches of rehabilitation plantations. Routine monitoring
on the survival and growth of the compensatory planting is required to monitor
the seedling performance throughout the monitoring period. Moreover, it is
agreed that LCSD will be responsible for the long-term maintenance and
management of this Wooded Area and Quarry Park throughout the operation phase.
Measures to minimize
direct impacts on fauna and flora species of conservation significance
13.3.15 Mitigation measures, including transplantation of any presence of floral
species of concern and translocation of fauna species of concern (namely
amphibians, freshwater crab and reptiles) found in the habitats within the
proposed development and works area, are proposed to minimize the ecological
impact on these flora and fauna groups. Prior to the site clearance works
and/or commencement of construction works, an updated vegetation survey will be
conducted in the habitats which are to be affected by the proposed construction
works. The survey will ascertain any presence, as well as update the
conditions, number, locations and habitat types of these species and other
rare/protected plant species (if any) identified within construction works areas. Any
identified floral species of concern will be properly protected and
transplanted (if practical and feasible) to the receptor site(s). The
transplanted specimens will be maintained throughout the construction phase to
ensure its establishment within the receptor site.
13.3.16 Prior to the site clearance
works, any water channels or streams that may be within the developable area of
the site should be searched by an
appropriately qualified ecologist. Any individual newts (or other species of conservation significance) found should be caught and relocated to a suitable
nearby location outside of the development area, such as an adjacent stream in the
Assessment Area where this species is known to be present.
Measures
to minimize impacts to hydrological condition and water quality of hillside
watercourses
13.3.17 Potential indirect impact during the construction phase may include
construction run-off or accidental spillage of chemicals, lubricants or
pollutants entering any seasonal or permanent wet watercourses identified to
the northeast, east and southeast of the Project, in which faunal species of
conservation importance were identified in the ecological surveys. The majority
of these watercourses are separated from the Study Area by Tai Sheung Tok Hill
and the major construction works will concentrate in the existing quarry site
and developed area. In addition, construction phase in situ mitigation measures are proposed to address these impacts
as detailed in the following:
(1) Temporary sewerage and drainage will be designed and installed to collect wastewater and prevent it from entering nearby watercourses;
(2) Proper locations well away from nearby watercourses will be used for temporary storage of materials (i.e. equipment, fill materials, chemicals and fuel) and temporary stockpile of construction debris and spoil, and these will be identified before commencement of works;
(3) To prevent muddy water entering nearby watercourses, work sites close to nearby watercourses will be isolated, using such items as sandbags or silt curtains with lead edge at bottom and properly supported props. Other protective measures will also be taken to ensure that no pollution or siltation occurs to the water gathering grounds of the works site;
(4) Stockpiling of construction materials, if necessary, will be properly covered and located away from nearby watercourses;
(5) Erection of temporary geotextile silt fences will be carried out around earth-moving works to trap any sediments and prevent them from entering watercourses;
(6) Construction debris and spoil will be covered and/or properly disposed as soon as possible to avoid being washed into nearby watercourses;
(7) Exposed soil will be covered as quickly as possible following formation works, followed, where appropriate, by covering with biodegradable geotextile blanket for erosion control purposes;
(8) Where appropriate, earth-bunding will be carried out of areas where soils have been disturbed or where vegetation has been cleared, to ensure that surface runoff will not move soils off-site;
(9) Construction effluent, site run-off and sewage will be probably collected and/or treated. Wastewater from any construction site will be minimised via the following in descending order: reuse, recycling and treatment;
(10) Proper locations for discharge outlets of wastewater treatment facilities well away from sensitive receivers will be identified and used;
(11) Silt traps will be installed at points where drainage from the site enters local watercourses;
(12) Appropriate sanitary facilities for on-site workers will be provided;
(13) The site boundary will be clearly marked and any works beyond the boundary strictly prohibited, and
(14) Regular water monitoring and site audit will be carried out at suitable points. If the monitoring and audit results show that pollution occurs, adequate measures including temporary cessation of works will be considered.
13.3.18 Accidental spillage events could potentially have a large impact on
nearby habitats in view of their susceptibility to such pollution. Therefore, an
emergency contingency plan should be established and implemented by the Project
Proponent or its delegate prior to construction, and will be in place at times
during the construction phase. The plan will include, but not be limited to,
the following:
(1) Potential emergency situation;
(2) Chemicals or hazardous materials used on-site (and their location);
(3) Emergency response team;
(4) Emergency response procedures;
(5) List of emergency telephone hotlines;
(6) Locations and types of emergency response equipment, and
(7) Training plan and testing for effectiveness.
Measures to minimize light disturbance impact on wildlife groups
13.3.19 Measures are proposed to minimize the potential indirect light
disturbance impact on the wildlife groups inhabiting the terrestrial habitats
surrounding the Project Site, especially affecting nocturnal mammals if
artificial lights are directed to these habitats. Mitigation measures include
but not limited to the following:
(1) Installation of environmentally-friendly lighting system in open space areas, landscaping areas, and commercial and recreational buildings in the proposed development;
(2) Avoid pointing light sources directly toward terrestrial habitats (i.e. plantations, secondary woodlands, shrubby grassland and watercourses) within and adjacent to the Study Area;
(3) Appropriate engineering design of the artificially lit areas and lighting system and consider options to reduce light pollution on the ecosystems, such as a limit the duration of lighting at night (high levels of lighting may not be necessary in the middle of the night), change the intensity of lighting, avoid sky glow and limit the number of intensively lit buildings by green building design, change the spectral composition of lighting, and reduce lights infringing into areas that are not intended to be lit; and
(4) Careful design of any lighting systems proposed for public and commercial uses on or nearby the plantations and secondary woodlands within the Project Site, where high diversity of fauna were identified.
Landscape and Visual
13.3.20 Design measures with intention to minimise
overall landscape and visual impact due to the development have been incorporated
into the layout plans during planning and design stages. Measures to further
avoid, as well as reduce and/or compensate the potential impacts during the construction
and operation of the Project have all been considered. These proposed
mitigation measures should be implemented as early as possible and many of
these perform multiple functions. A summary of the proposed mitigation measures
for the design, construction and operational phase of the Project are
summarised in Tables 13.2 to 13.4 below:
Table 13.2: Design phase
mitigation measures
ID
No. |
Design
Measures |
DM1 |
Control of building heights to preserve the ridgelines of
Tai Sheung Tok |
DM2 |
Creation of extensive pedestrian
linkages and open space network system connected to Kwun Tong Region. |
DM3 |
Preservation
of high landscape value, rehabilitation zone and enhancement on Quarry Berms |
DM4 |
Incorporation of visual
connections and breezeways through preserve of visual corridor and natural
air flows |
DM5 |
Proper disposition of building mass and avoidance of excessive height and bulk of site building and structure
to minimise intrusive views to visual resources. |
DM6 |
Proper design of road layout and streetscape, open space
network in adjacent areas |
DM7 |
Tree Preservation/
Removal/ Transplanted Application should be obtained prior to implementation
at early design stage in accordance with ETWB TCW No. 29/2004, 10/2013 and LAO GN No.
7/2007 |
DM8 |
Greening Provision
in the early project planning stage in accordance with DEVB TCW
No. 2/2012 and
PNAP APP-152 |
DM9 |
ACABAS submission upon
completion of conceptual design should be accordance with ETWB TCW
No. 36/2004 |
DM10 |
Maintenance
responsibilities should be obtained agreement with concerned party in accordance with ETWB TCW
no. 2/2004 |
Table 13.3: Construction phase mitigation measures
ID No. |
Construction Phase Mitigation Measures |
Funding /
Implementation |
Maintenance/
Management Agency |
CM1[3] |
All existing
trees to be retained shall be carefully protected during construction. |
CEDD |
CEDD |
CM2[2] |
Tree
Transplantation - Should removal of trees be unavoidable due to construction
impacts, trees will be transplanted or felled. Detailed transplanting
proposal will be submitted to relevant government departments for approval in
accordance with LAO GN No. 7/2007, ETWB TCW No. 29/2004 and 10/2013. Final locations
of transplanted trees shall be agreed prior to commencement of the
work. |
CEDD |
CEDD (Until handover to relevant government departments) |
CM3[3] |
Control of
operation night-time glare with well-planned lighting
operation strategy to minimize potential glare impact to adjacent VSRs. |
CEDD |
CEDD |
CM4[3] |
Erection of decorative screen hoarding. |
CEDD |
CEDD |
CM5[1] |
Minimise
disturbance and limitation of run-off – temporary structures and construction
works should be planned with care to minimise disturbance to adjacent
landscape, vegetation, natural stream habitats. |
CEDD |
CEDD |
Notes:
[1] The maintenance of the interim greening measures will be undertaken by contractor for the first 12-month establishment period. In the case that the site is still not allocated after the establishment period, CEDD would liaise with relevant government departments to agree on the subsequent maintenance agent of the interim greening measures. Contractor would be responsible for the maintenance of the interim greening measures before any agreement is made.
[2] The management and maintenance agencies of mitigation measures have been identified in accordance with ETWBTC 2/2004. The agreement and approval of the implementation, management and maintenance agencies of the Project will be sought from relevant parties during detailed design stage of the project. Contractor would be responsible for maintenance and management of trees, vegetation and the associated facilities (e.g. irrigation system) within the permanent site boundary. The maintenance matrix and responsible parties for trees outside the permanent site boundary are yet to be confirmed. To facilitate with the confirmation process, CEDD would be responsible for the maintenance works before any agreement is made.
[3] Mitigation measures refer to Good Site Practices.
Table 13.4: Operational phase
mitigation measures
Notes:
[1] The maintenance of the interim greening measures will be undertaken by contractor for the first 12-month establishment period. In the case that the site is still not allocated after the establishment period, CEDD would liaise with relevant government departments to agree on the subsequent maintenance agent of the interim greening measures. Contractor would be responsible for the maintenance of the interim greening measures before any agreement is made.
[2] The management and maintenance agencies of mitigation measures have been identified in accordance with ETWBTC 2/2004. The agreement and approval of the implementation, management and maintenance agencies of the Project will be sought from relevant parties during detailed design stage of the project. Contractor would be responsible for maintenance and management of trees, vegetation and the associated facilities (e.g. irrigation system) within the permanent site boundary. The maintenance matrix and responsible parties for trees outside the permanent site boundary are yet to be confirmed. To facilitate with the confirmation process, CEDD would be responsible for the maintenance works before any agreement is made.
[3] Mitigation measures refer to Good Site Practices.