Table of Contents
8. landscape &
visual impact assessment
8.7 Consultation with Relevant
Departments
8.8 Methodology for Landscape
Impact Assessment
8.10 Magnitude of Landscape
Impacts
8.11 Significance of the
Landscape Effects
8.12 Visual Assessment Methodology
8.14 Environmental Legislation
and Guidelines
8.15 Planning & Development
Review
8.16 Baseline Conditions (Year
2011)
8.19 Landscape and Visual Effect
Assessment Methodology
8.20 Landscape Resource (LR)
effects
8.21 Landscape Character Area
(LCA) effects
8.23 Visual Sensitive Receivers
(VSRs)
8.26 Environmental Monitoring
and Audit
8. landscape & visual impact
assessment
8.1 Introduction
8.2 Standards and Legislation
8.3 General Approach
8.4 Terminology
8.5 Impact Assessment
8.6 The Study Area
8.7 Consultation with Relevant Departments
8.8 Methodology for Landscape Impact Assessment
8.9 Landscape Sensitivity
8.10 Magnitude of Landscape Impacts
8.11 Significance of the Landscape Effects
8.12 Visual Assessment Methodology
8.13 Mitigation
8.14 Environmental Legislation and Guidelines
8.15 Planning & Development Review
8.16 Baseline Conditions (Year 2011)
8.17 Landscape Resources (LR)
8.18 Landscape Character Area
8.19 Landscape and Visual Effect Assessment Methodology
8.20 Landscape Resource (LR) effects
8.21 Landscape Character Area (LCA) effects
8.22 Visual Effects
8.23 Visual Sensitive Receivers (VSRs)
8.24 Mitigations
8.25 Residual Impacts
8.26 Environmental Monitoring and Audit
8.27 Summary of Conclusions
8. landscape & visual
impact assessment
8.1 Introduction
8.2 Standards
and Legislation
8.3 General
Approach
8.4 Terminology
8.5 Impact
Assessment
8.6 The
Study Area
8.7 Consultation
with Relevant Departments
8.8 Methodology
for Landscape Impact Assessment
8.9 Landscape
Sensitivity
8.10 Magnitude
of Landscape Impacts
8.11 Significance
of the Landscape Effects
8.12 Visual
Assessment Methodology
8.13 Mitigation
8.14 Residual Impacts8.14 Environmental Legislation
and Guidelines
8.15 Environmental Monitoring and Audit8.15 Planning &
Development Review
8.16 Summary of Conclusions8.16 Baseline Conditions (Year
2011)
8.17 Planning & Development Review8.17 Landscape Resources (LR)
8.18 Baseline Conditions (Year 2011)8.18 Landscape Character Area
8.19 Projected Landscape Baseline (Year 2011)8.19 Landscape and Visual
Effect Assessment Methodology
8.20 Landscape
Resources (LR) effects
8.21 Landscape
Character Area (LCA) effects
8.22 Visual
Effects
8.23 Mitigations8.23 Visual Sensitive
Receivers (VSRs)
8.24 Residual Impacts8.24 Mitigations
8.25 Environmental Monitoring and Audit8.25 Residual Impacts
8.26 Summary of Conclusions8.26 Environmental Monitoring
and Audit
8.27 Summary of Conclusions
List
of Tables
Table 8‑1 Classification of Landscape Sensitivity
Table 8‑2 Classification
of Magnitude of Landscape Impact
Table 8‑3 Levels
of Significance
Table 8‑4 Numbers
of Tree Schedule for Felling, Transplanting and Compensation
Table 8‑1 Classification of Landscape Sensitivity
Table 8‑2 Classification of Magnitude of Landscape
Impact
Table 8‑3 Levels of Significance
Table
8‑4 Numbers of Tree Schedule for
Felling, Transplanting and Compensation
Table 8‑4 Degree of Residual Impacts
List
of Figures
Figure 8.1 Tsuen
Wan Outline Zoning Plan (Plan No. S/TW/2425)
Figure 8.2 Kwai
Chung Outline Zoning Plan (Plan No. S/KC/21)
Figure 8.3
Baseline Landscape
Resources & Landscape Character Areas and
Photographs
Figure 8.3a Landscape
Character Areas (On Site Photos)
Figure 8.4 Visual
Envelope
Figure 8.4a Zone
of Visual Influence and Key Visual Sensitive Receptors (VSRs)
Figures 8.5 to 8.9 Conceptual Landscape Layout
Figure 8.10a Conceptual Landscape Layout and
Photomontages – 1
Figure 8.10b Conceptual Landscape Layout and
Photomontages – 2
Figure 8.10c Conceptual Landscape Layout and
Photomontages – 3
Figure 8.10d Conceptual Landscape Layout and
Photomontages – 4
Figure 8.10e Conceptual Landscape Layout and
Photomontages – 5
Figure 8.11 Schedule of Landscape
Resources & Characters Effects
Figure 8.12 Schedule of Landscape Visual
Effects
Figures 8.13 to 8.15 Road Cross Sections
Figure 8.16 Details of Bridge Deck
Planter
Figure 8.17 Details of Planter at Bridge
Pier
Figure 8.18 Images of Propose Planter
Figure 8-.19 Tree
Surevy Plan
Appendix
Appendix 8-A Tree Schedule
Appendix 8-B Conceptual Planting Plan
8.1.1
This section of the EIA report seeks to establish
the landscape and visual effects of the construction and operation of the
upgraded Tsuen Wan Road. The assessment process identifies the current and
projected baseline conditions, the effects of the road widening upon the
landscape resource and visual receptors within the road corridor and the
landscape mitigation measures proposed in order to reduce significant effects.
8.1.2
A description of the development
proposals is included elsewhere in this environmental statement, whilst Figures 8.5 to 8.9 demonstrate the Conceptual Landscape ProposalsLayouts.
8.2.1
The following legislation, standards and
guidelines are applicable to the appraisal of landscape and visual impacts and
the design of mitigation measures in Hong Kong:
·
EnvironmentEnvironmental Impact
Assessment Ordinance (Cap. 499. s.16) and the Technical Memorandum on EIA Process
(EIAO TM), particularly Annexes 3, 10, 18, 20 and 21;
·
Hong Kong Planning Standards and
Guidelines Chapter 10, ‘Conservation’;
·
Hong Kong Planning Standards and
Guidelines Chapter 4, ‘Recreation, Open
Space’ and Greening’;
·
Works Branch Technical Circular (WBTC)
No. 25/93 – ‘Control of Visual Impact of Slopes’;
·
WBTC No. 25/92 – Allocation of Space for
Urban Street Trees;
·
WBTC No.
17/2000 – Improvement to the Appearance of Slopes;
·
CED (GEO) – GEO Publication No. 1/2000 –
Technical Guidelines on Landscape Traetment and Bio-Engineering for Man-made
Slopes and Retaining Walls; and
·
WBTC No.
7/2002 – Tree Planting in Public Works.
8.2.2
The assessment method has, however, been further
refined in accordance with contemporary guidance (“Guidelines for . EIAO Guidance Note No. 8/2002 –
Preparation of Landscape & and Visual Impact Assessment for under the Environmental Impact Assessment, published
by the UK Landscape Institute & the Institute of Environmental Management
and Assessment – First Edition 1995 and Second
Edition 2002) and Scott Wilson’s own
methodology developed over a 20 year period Ordinance.
8.3.1
For the purposes of the environmental
assessment process, a clear distinction is drawn between landscape and visual
impacts:
·
Landscape impacts:
relate to the impacts of the proposed Scheme’s construction and operation, upon
the physical characteristics or components of the landscape. Together these
form the character of that landscape e.g. landform, vegetation, and buildings.
·
Visual impacts:
relate to the changes arising from development to individual ‘receptors’ views
of that landscape e.g. local residents or passing motorists.
8.4.1
Landscape – comprises those physical
components, which together form the appearance of land, including its shapes,
colours and textures. Landscape also reflects the way in which these various
components combine to create distinctive landscape character, particular to
specific localities.
8.4.2
Study Area – is the area within which
desk and site surveys have been carried out when determining the extent of the
influence of development upon the adjoining landscape.
8.4.3
Zone of Visual Influence – the extent of
the Study Area is principally determined by the definition of a Zone of Visual
Influence (ZVI), within which views of the proposed development may be
achieved. The extent of the ZVI is determined by many factors including
topography and intermediate visual intrusions such as buildings and blocks of
woodland, which create areas of visual “dead ground.”
8.4.4
Landscape Character Areas – Landscape
Character Areas (LCA’s) are areas of homogenous landscape character. Typical
landscape components defining character include land use, built form, landform
& vegetation.
8.4.5
Visual Receptors – within the ZVI key
viewpoints from publicly accessible roads, footpaths and other open spaces are
identified e.g. Tsuen Wan Park. Individual
visual receptors groups within the ZVI are also identified and categorised in
terms of their sensitivity to visual change e.g. local residents and passing
motorists.
8.4.6
Baseline Conditions – the baseline
landscape and visual conditions were most recently assessed through both desk
and site appraisal during March 2003. The baseline conditions were assessed in
terms of:
·
Planning and development context;
·
Landscape context;
·
Landform;
·
The existing road;
·
Land use;
·
Vegetation (a tree survey of the road
corridor has been undertaken);
·
Landscape features
8.5.1
For the purposes of comparison and in
order to establish a ‘control’ scenario against which impacts may be assessed,
the baseline conditions are projected forwards to produce a 2011 baseline, which incorporates
known future developments. The key
potential impacts of the proposed development (“the Scheme”) upon the baseline
landscape, and identified receptor groups’ views of that landscape, are then
identified and assessed.
8.5.2
Through the assessment of impacts at
three points in time: during construction (2011-2015), on operation Day 1 (2015)
and in Year 10 of operation (2025), distinctions may be drawn between temporary,
permanent, short-term and long-term impacts. Landscape and visual impacts may
be further categorised as being either direct impacts i.e. within the Study
Area as defined by the ZVI, or indirect impacts e.g. off site visual impact of construction traffic.
8.1.1
8.1.1
The “no development” scenario,
should the upgrading not proceed, is also briefly examined.
8.6.1
The Study Area for the assessment of the
landscape impact is within 100m from the Project boundary and visual impacts
is largely defined by the Visual Envelope (Refer to Figure 8.4). This defines
the extent of the route corridor within which views of the upgraded road or its
passing traffic, lighting or associated signage may be achieved.
8.6.2
The Zone of Visual Influence (ZVI) for
this Scheme is defined by a Primary ZVI within which the visual effects of the
new road may be significant as a consequence of proximity or the elevation of
the receptor’s viewpoint. e.g. residents of Clague Garden Estate. The effects upon visual receptors within a Secondary
ZVI e.g. residents on Tsing Yi Island, are assessed as insignificant, as a consequence of distance and the upgraded road’s
low impact in forming a relatively minor component within the wider urban landscape.
The Primary ZVI has been established by initial analysis of topographic and
other maps, subsequently verified by field survey.
8.7.1
Relevant Government Departments,
including PlanD, CEDD, LCSD and EPD have been consulted throughout the study
process.
8.8.1
For the purposes of structuring the
assessment of landscape effects of the Scheme, the Study Area has been
subdivided into areas of discrete urban landscape character (LCA’s) on the
basis of the baseline studies and surveys.
8.8.2
Landscape impacts include the direct and
indirect impacts of the Scheme upon the physical landscape features of the
Scheme corridor and the aggregated impact of these changes upon the character
of each LCA. Landscape impacts are, therefore, assessed at three levels:
·
Firstly, in terms of systematic
consideration of impact upon landscape features;
·
Secondly, in terms of aggregate impact
upon a LCA;
·
Thirdly, in terms of overall long-term
impact within 100m from the ZVIProject boundary.
8.9.1
The sensitivity of the landscape to
change is the degree to which a particular LCA can accommodate changes or new
features without unacceptable detrimental effects to its essential
characteristics. Criteria used in this study to determine the sensitivity of
landscape character include:
·
The distinctiveness of character and
quality of the existing urban landscape;
·
The vulnerability of the key components
determining character;
·
The nature of predicted impacts, the
degree of change that would result and the ability of the landscape to
accommodate that change; and
·
The significance of the landscape
resource in a local, regional and national context;
·
The maturity of the landscape.
8.9.2
Table
8.1 identifies typical criteria used to define
sensitivity to change as set out in the Guidelines for Landscape and Visual
Impact Assessment (LI/IEA, 1995).
Table 8‑1 Classification of Landscape Sensitivity
Description |
Sensitivity |
For example, important components or
landscape of particularly distinctive character susceptible to relatively
small changes. |
High |
For example, a landscape of moderately
valued characteristics reasonably tolerant of change. |
Medium |
For example, a relatively unimportant
landscape, the nature of which is potentially tolerant of substantial change.
|
Low |
8.10.1
The magnitude of a landscape impact
relates to:
·
the size, extent or degree of change to
landscape character or individual landscape components.
·
whether there is a direct impact
resulting in the loss of landscape components, or change beyond the landtake of
the Scheme having an impact on the character of the area, and
·
whether the impact is permanent or
temporary;
·
the reversibility of change.
8.10.2
Table
8.2 identifies typical criteria used to define
magnitude of change, as set out in the Guidelines for Landscape Visual
Assessment Impact Assessment (LI/IEA, 1995).
Table 8‑2 Classification of Magnitude of Landscape
Impact
Description |
Magnitude |
Notable change in landscape
characteristics over an extensive area ranging to very intensive change over
a more limited area. |
Large |
Moderate change in localised area |
Intermediate |
Virtually imperceptible change in any
component |
Small |
No change in any component |
Negligible |
8.10.3
Combined impacts are assessed as very
substantial, substantial, moderate, slight and negligible impacts are termed
negligible. A matrix is used to assess
landscape impacts and is shown in the Table
8-2a below:
Table 8-2a Assessment Matrix for Landscape
Impact
Magnitude of Change |
Sensitivity of Landscape Resource/Character |
||
High |
Medium |
Low |
|
Large |
very substantial to substantial |
substantial to moderate |
moderate to slight |
Intermediate |
moderate |
slight to very slight |
|
Small |
moderate to slight |
slight to very slight |
very slight to negligible |
Negligible |
negligible |
negligible |
negligible |
Combined impacts are assessed as very
substantial, substantial, moderate, slight and negligible impacts are termed
negligible. A matrix is used to assess
visual impacts and is shown in Table 8-2b
below:
Table 8-2b Assessment Matrix for Visual Impact
Magnitude of Change |
Sensitivity of Receiver Group |
||
High |
Medium |
Low |
|
Large |
very substantial to
substantial |
substantial to moderate |
moderate to slight |
Intermediate |
substantial to moderate |
moderate |
slight to very slight |
Small |
moderate to slight |
slight to very slight |
very slight to negligible |
Negligible |
negligible |
negligible |
negligible |
8.11.1
The significance of the effect of the
Scheme on each LCA is determined by combining the magnitude of the effect with
the sensitivity of each area to change. Criteria used to derive significance
are illustrated in the Table 8.3,
which is based on Annex 10 of the EIAO-TM.
Table 8‑3 Levels
of Significance
The evaluation of landscape and visual impact may be
classified into five levels of significance based on type and extent of the
effects concluded in the EIA study: |
The
|
|
|
|
The impact is undetermined if significant adverse
effects are likely, but the extent to which they may occur or may be
mitigated cannot be determined from the study. Further detailed study will be required for the specific
effects in question. |
8.11.2
* Residual Impacts - In accordance with Annex 10
of the EIAO-TM an overall assessment is also made of the residual landscape and
visual impacts attributable to the proposed scheme. The degree of residual impact is defined as shown in Table 8.3.
8.11.3
The significance of the effect on each
landscape character area is stated during construction (2011-2015), on day 1 of
operation (Year 2015) and ten years later (i.e. 2025). The significance of the
effect in Year 2025 is judged against the future predicted baseline and takes
into account those developments within the road corridor, which are likely to
occur over this period.
8.11.4
In accordance with the
Environment, Transport & Works Bureau Technical Circular (Works) No.
3/2006, Tree Preservation, a full tree survey has been carried out adjacent to
the existing road. A tree survey was carried out in 2008 by
Scott Wilson Ltd. which identified all tree and palms (with girth diameter
exceeding 95DBH). Proposals for
retention, transplantation or felling of trees were put forward. A total of 375, 243 and 589 trees were scheduled for felling,
transplanting and retaining respectively (refer to Appendix 8-A). The locations of affected trees/palms are shown in Figure 8-19. The affected trees including native and
exotic tree species have been identified in the Tree Survey. Compensatory planting schedule is outlined in the
Tree Survey.
8.11.5
According to the tree
survey, dominant native tree species include: Albizia lebbek, Bauhinia
purpurea, Hibiscus tiliaceus Macaranga tanarius and Peltophorum
pterocarpum. On the other hand,
dominant exotic trees species include: Acacia confusa, Casuarina
equisetifolia, Eucalyptus citriodora and Eucalyptus robusta. No Old and Valuable Trees (OVT) as set out
in ETWB TCW No. 29/2004 was identified within the study area.
8.11.6
The mitigation measures
include:
·
retention of 589 trees,
·
transplantation of a
total number of 243 trees
·
landscape works including
375 compensatory trees
following completion of the Project. Compensatory planting is provided in the
Tree Survey – “CONCEPTUAL PLANTING PLAN” (refer to Appendix 8-B):
All transplanting trees
and compensatory trees (i.e. 618 trees) shall be planted within the Project site
and properly maintained during operation of the Project. Any of these
trees damaged during operation of the Project shall be replaced. Details of compensatory
planting such as detailed location and compensatory plant species will be
decided at the design stage. It is recommended, as stipulated in ETWB TC(W) No.3/2006 Tree
Preservation, that the implementation of compensatory plant should not be
less than 1:1 (i.e. not less than 375 nos. of trees in this project) and the
compensatory planting trees should be at least of “heavy standard” type.
8.11.7
Table 8-4 summarizes the numbers
of tree schedule for felling, transplanting and compensation.
Table 8‑4 Numbers of Tree Schedule for Felling,
Transplanting and Compensation
No. of tree to be
felled |
No. of tree to be
transplanted |
No. of compensatory
tree |
375 |
243 |
|
4473753416891891447375
8.12.1
The assessmentAssessment of visual
impacts is
are structured
by receptor groups.
Individual receptors are identified through the definition of the ZVI, within
which views of the development may be possible, and the subsequent
categorisation of individuals into ‘receptor groups’ within that envelope. The
sensitivity of each receptor group is categorised as being high, medium or low.
‘Development’ can include passing vehicles, night lighting and signage.
8.12.2
Visual impacts result from change to the
appearance of the urban landscape as a result of the development proposals
either intruding into, or obstructing existing views, or by their overall
impact on visual amenity and character. The sensitivity of receptors relates principally to four factors:
·
Receptor’s function whilst exposed to
view;
·
Degree of exposure to view;
·
Period of exposure to view; and
·
Number of receptors.
8.12.3
The criteria used to assess the magnitude
of visual effects are as follows:
·
value of existing views;
·
degree of change to existing views;
·
the availability and amenity of the alternative
views;
·
distance of receptor;
(effects may be considered as beneficial
i.e. positive as well as adverse.)
8.12.4
Whilst there is professional judgment inherent in determining the
category of effect, the assessment process is both systematic and structured.
The effect category being broadly determined by the interaction of the
magnitude of impact and the sensitivity of the receptor.
8.12.5
The criteria detailed above can be combined to assess the effects that
development would have upon the existing baseline visual conditions for a given
receptor and defined impact thresholds.
Effects are categorized into the 5 levels of significance as identified
in Annex 10 of the EIAO-TM (See Table 8.3).
8.13.1
The Conceptual Landscape Proposals (Figures 8.5 to 8.10d9) indicate, inter
alia, those landscape measures, which are proposed to mitigate significant
visual and landscape effects identified through the assessment process. These measures include:
·
RegradingRegarding of cut slopes
·
Revegetation of chunam slopes
·
Tree planting including Tree Preservation Proposal
·
Screen walls
·
Feature finishes to structures and floorscape
·
Provision of new recreational/amenity
facilities
·
Amenity shrub, ground cover and climber
planting
8.1.1In
accordance with Annex 10 of the EIAO-TM an overall
assessment is also made of the residual landscape and visual impacts
attributable to the proposed scheme.
The degree of residual impact is defined as shown in Table 8.4.
Table 8‑4 Degree
of Residual Impacts
|
|
|
|
|
|
|
|
|
|
8.14.1
Landscape and visual mitigation design
aspects of this project will be in accordance with the following guidelines:
·
Hong Kong Planning Standards and
Guidelines;
·
Tree Preservation, (Works Branch), WBTC
No. 3/2006;
·
Maintenance of Vegetation and Hard
Landscape Features (Works Branch), WBTC No. 2/2004;
·
Control of Visual Impact of Slopes (Works
Branch), WBTC No. 25/93;
·
Improvement to the Appearance of Slopes
(Works Branch), WBTC No. 17/2000;
·
Updating of GEO Publication no. 1/2000 -
Technical Guidelines on Landscape Treatment and Bio-engineering for Manmade
Slopes and Retaining Walls (GEO Publication No.
6/2007);
·
Allocation of Space for Urban Street
Trees (Works Branch). WBTC No. 25/92;
·
The Advisory Committee on the Appearance
of Bridges and Associated Structures (ACABAS),
WBTC No. 36/2004;
·
Visibility of Directional Signs,
HyDTC 10/2001; and
8.1.1
The assessment process is
completed by consideration of the environmental monitoring and audit procedures
proposed for both the construction and operational phases of the upgraded road.
8.1.1
The assessment process is
completed by consideration of the environmental monitoring and audit procedures
proposed for both the construction and operational phases of the upgraded road.
8.15.1
Whilst the redevelopment of obsolete
residential and industrial sites has provided the major development initiative
in Tsuen Wan, there has been a shift in development focus from the established
town centre towards the waterfront. The
construction of the MTR West
Rail Station, the TW5, 6 & 7 residential developments will transform the
urban landscape character of the road corridor as it passes to the west of
Tsuen Wan Town centre.
8.15.2
The Tsuen Wan Road corridor passes
through two planning areas:
·
North of Tsuen Wan Road falls within the
Tsuen Wan Outline Zoning Plan Area (Figure 8.1)
·
South of Tsuen Wan Road passes through
the Kwai Chung Outline Zoning Plan Area (Figure 8.2)
8.15.3
The Outline Zoning Plan for Tsuen Wan was
exhibited for public inspection under Section 7 of the Ordinance on 6 July 200711 April 2008. The objectobjective of the plan is
to indicate the broad land use zonings and major road networks within which the
development and redevelopment of land can be put under statutory control. The plan illustrates the broad principles of
development and provides guidance for more detailed planning within the planning
scheme area.
8.15.4
The Planning Scheme Area (the Area),
about 743 hectares in size covering Tsuen Wan Valley and its adjoining areas,
forms a part of Tsuen Wan New Town. It is located at the southern coast of the
New Territories some 16 km by road from Tsim Sha Tsui, / Kowloon. The Area
extends from Wo Yi Hop Road in the east to Yau Kom Tau in the West. The Area is the most densely populated part
of the Tsuen Wan District Council area. For planning and reference purposes,
the Area is subdivided into a number of smaller Planning Areas, each with an
area number, which are referred to below.
8.15.5
The areas to the south of Castle Peak
Road were reclaimed from the sea between the late 1950's and early 1960's and
were mostly developed in 1960's.
8.15.6
The Tsuen Wan Central Area could be
divided into a number of sub-areas, which are attributable to their individual
characteristics. The town centre is mainly a commercial/residential area with
provisions of various regional and district community facilities. The old town
centre area used to be around Sha Tsui Road and Yeung Uk Road. With completion
of the MTR Tsuen Wan Line, the bulk of development activities has taken place around
the MTR development at Luk Yeung Sun Chuen. The provision of major community
facilities, such as ferry and bus terminus, the Tsuen Wan Town Hall and
Magistracy, and future commercial/office development sites are located in the
southern part of the area, adjacent to the old town centre. A strip of area to
the south of Tsuen Wan Road was reclaimed and developed for the West Rail Tsuen
Wan West Station. It is therefore considered desirable to link up the two old
and new commercial/residential cores at the northern and southern ends of the
town through a well-integrated footbridge system.
8.15.7
The expansion of Tsuen Wan has resulted
in a number of large scale comprehensive major residential redevelopments from
old industrial lots at the fringe of the town, namely Bayview Garden, Belvedere
Garden, The Panorama, Serenade Cove, Discovery Park, Waterside Plaza and
Riviera Gardens. Sandwiched between the old and new commercial/ residential
cores are two main industrial areas at Chai Wan Kok and Yeung Uk Road/Texaco Road.
8.15.8
To the north of the town centre area
abutting the foothill of Tai Mo Shan lies a number of village zones and green
belt areas inside which several monasteries like Chuk Lam Sim Yuen and Yuen
Yuen Hok Yuen, and the recreational Hilltop Country Club are located.
8.15.9
A site which is occupied by industrial
developments in Planning Areas 24 is zoned ‘CDA’ ie. “Comprehensive Development
Areas”. Such zoning is primarily intended to encourage the phasing out of these
industrial activities, which have become incompatible with the adjoining
residential developments. In the meantime, however, the existing factories will
remain without conforming to the zone and application can be made to the Board
for other uses which are more compatible with their neighbouring uses and would
result in improvement to the environmental quality of the area. Industrial
installations or structural alterations of existing factory buildings aiming at
mitigating the pollution impacts of the industries upon their neighbouring
areas are also welcome and normally would be permitted on application.
8.15.10 The
area at the West Rail Tsuen Wan West Station and some adjoining sites in
Planning Areas 22 and 25 are designated as three separate "CDA "
zones to facilitate the implementation of comprehensive commercial and
residential developments at and around the Tsuen Wan West Rail Station and the
associated public
Transport interchange.
8.15.11 For
the "CDA" zones associated with the West Rail Tsuen Wan West Station,
a maximum non-domestic/domestic plot ratio of 9.5/5 is imposed which generally
accords with the plot ratio control that has been incorporated in most of the
lease conditions for new commercial/residential lots in Tsuen Wan.
8.15.12 Pursuant
to section 4A(1) of the Ordinance, any development in the "CDA" sites
would require the approval of the Board through planning application under
section 16 of the Ordinance. The applicant shall prepare a Master Layout Plan
(MLP) together with an environmental impact assessment, a traffic impact
assessment and other materials as specified in the Notes of the Plan for
approval by the Board pursuant to section 4A(2) of the Ordinance. This will
ensure that development proposals would be designed in a comprehensive manner
taking into account various planning considerations such as environmental
quality, neighbourhood compatibility, provision of shopping, community and
recreational facilities as well as traffic and phasing requirements. When
approved by the Board, a copy of the approved MLP certified by the Chairman of
the Board shall be deposited in the Land Registry and made available for public
inspection pursuant to section 4A(3) of the Ordinance.
8.15.13 The
areas through which the Tsuen Wan Road passes are undergoing extensive change
as a consequence of the redevelopment of the existing “first generation” new
town fabric, the construction of the MTR West Rail immediately to the west of
the Tsuen Wan Road. The urban landscape of the road corridor will, therefore,
be transformed during the period of the Road upgrading i.e. by 2011. The Planning Areas adjoining the Tsuen Wan Road
are Nos, 2, 3 19, 22, 24, 25 & 35.
8.15.14 Planning Area 2
comprises an area of high-rise residential blocks on either site of the Castle
Peak Road which currently adjoin and overlook the Rambler Channel to the south
and the Tsuen Wan Road corridor to the south east. At the extreme eastern end of this Area, a new MTR ventilation
building has recently been constructed adjoining the road, whilst the “captured”
Kong Nam Industrial Building is now zoned for “Business” use and is, therefore,
a non-conforming land use in this increasingly residential area and is, as
such, liable to redevelopment.
8.15.15 Planning Area 3,
where it adjoins the western end of the Tsuen Wan Road at its junction with the
Tuen Mun Road, comprises a sequence of cut slopes which form a prominent wooded
backdrop to the urban area and a visual buffer to the hill slopes of the Tai Mo
Shan Country Park to the north and west.
An open area immediately to the east of the cut slopes is mainly zoned
Residential (Group A) and occupied by a residential development known as Summit
Terrace.
8.15.16 Planning Area 19
(the Chai Wan Kok Industrial Area) predominantly comprises a number of large
scale, high rise industrial units, although a small park exists at the junction
of Tai Chung Road and Hoi Shing Road.
8.15.17 Planning Area 22
forms parts of Tsuen Wan’s town centre and includes a mixture of uses including
the new Town Hall, the Tsuen Wan Plaza, the Clague Garden Estate and Tsuen Wan Transport
Complex, which both immediately adjoin the elevated Road.
8.15.18 Planning Area 24 to the east of the Road,
comprises the Industrial buildings along Tsuen Wan Road, where a maximum plot
ratio of 9.5 is defined for industrial unit redevelopment. The triangular site at the interchange of
the Tsuen Wan Road, Texaco Road and Ma Tau Pa Road is zoned for Government, Institution
or Community use.
8.15.19 Planning Area 25
is formed by the Tsuen Wan Bay South area of reclamation between the Tsuen
Tsing Interchange and Tsuen Wan Road.
This large area has been built out for a mixture of public and private
high rise housing on either side of Wing Shun Street. The cleared West Rail reserve corridor currently separates the
Waterside Plaza from the Road. However,
future residential development over the MTR reserve will provide a buffer
between the existing residential blocks and the widened Tsuen Wan Road.
8.15.20 Planning Area 35
straddles the central section of the Tsuen Wan Road. The area to the east of the road comprises Tsuen Wan Park and the
large scale commercial/residential developments – currently under construction
between the park and Yeung Uk Road (Nina Tower, the LDC Development and possible
future Hotel Development). To the west
of the Tsuen Wan Road, which is on structure throughout the Tsuen Wan Outline
Zoning Plan area, lies the MTR reserve which currently includes the new Tsuen
Wan West Station and Tsuen Wan Pier.
Extensive new development is planned on a series of sites over and
adjoining the MTR tunnel (see Section 16 Application for Development).
8.15.21 The
Zoning Plan also shows Tsuen Wan Park extending beneath the Tsuen Wan Road across
the MTR tunnel corridor to form a continuous promenade along the Rambler
Channel Linking Riviera Park in the south with West Rail Tsuen Wan West Station
in the north (Tsuen Wan Park Phase 2).
8.15.22 The
Kwai Chung Outline Zoning Plan (OZP) was approved on 29 June 2004 and
represents, therefore, up to date government policy. The object of the Plan
being to indicate broad land use zonings and major transport networks so that
the development and redevelopment of land in Kwai Chung can be put under
statutory planning control. The Plan
also provides for the integration of development proposals in Kwai Chung with
those in other parts of Tsuen Wan New Town.
8.15.23 The
Planning Scheme Area (the Area) covers an area of about 1,025 hectares (ha). It
is situated in Tsuen Wan New Town Within the Kwai Tsing Administration
District. It includes various parts of Kwai Chung Valley to the north-east and
the container terminals on reclaimed land to the south-west. To the east, the
Area adjoins the Kam Shan Country Park, whilst to the south, it is bounded by
Ching Cheung Road. To the west, the Area is bounded by the sea, whilst to the
north, it is delimited by Tsuen Tsing Interchange, Texaco Road, Castle Peak
Road, Wo Yi Hop Road and Cheung Pei Shan Road. The boundary of the Area is
shown in a heavy broken line on the Plan. For planning and reference purposes,
the Area is subdivided into a number of smaller planning areas, each with an
area number, which are shown on the Plan.
8.15.24 Most
of the flat land in Kwai Chung has been formed by reclaiming the adjacent
seabed with fill materials excavated from nearby hills, which in turn have been
formed into levelled platforms for building developments.
8.15.25 As
an integral part of Tsuen Wan New Town, Kwai Chung provides housing,
employment, recreational, cultural and other community facilities to the
residents of the New Town as a whole and also in turn relies on certain
facilities which are, or will be, provided elsewhere in the New Town. It also accommodates some of the major
facilities of territory-wide significance, such as the container terminals.
8.15.26 The
Tsuen Wan Road between the Tsuen Tsing Interchange and Kwai Tsing Interchange
passes between a number of sharply contrasting Planning Areas (Nos 26, 37 &
38).
8.15.27 Planning Area 26
comprises a visually prominent and diverse collection of land uses located on a
natural headland. The area would have formed a conspicuous feature projecting
out into the Rambler Channel.
8.15.28 The
exposed, east facing hillside which defines the Tsuen Wan Road corridor within
Area 26 comprises an unsightly collection of industrial units, chunam rendered
cut slopes and platforms used for container storage. This area remains zoned for industrial use although future
development of industrial units will be limited to a plot ratio of 9.5. Beyond the existing industrial units the
Chinese cemetery is glimpsed between buildings.
8.15.29 Planning Area 37 as
it adjoins the southern end of the Tsuen Wan Road, comprises the wooded flanks
of the closed Gin Drinkers Bay landfill, which has now been restored to form
Kwai Chung Park. This park, however,
has yet to be opened to the public.
8.15.30 Planning Area 38
defines the road corridor between Tsuen Tsing Interchange and Kwai Tsing Interchange
to the east and is zoned for industry.
Whilst a number of industrial premises to the east of the Road have been
recently redeveloped to industrial uses, further potential industrial
development sites exist over the MTR West Rail tunnel off the Kwai Fuk Road and
in the strip of land between Kwai Hei Street and the Tsuen Wan Road.
8.16.1
Located to the west of Kowloon in the New
Territories, on the east bank of the Rambler Channel, Tsuen Wan was Hong Kong’s
first generation new town built in the early 1960’s. As such, elements of the urban fabric, including many of the
original industrial ‘go downs’, are now in need of redevelopment, creating an
opportunity to improve environmental standards and resolve interface conflicts
between residential and industrial uses.
The new town is, therefore, undergoing a period of intense change and ‘regeneration’
with new social infrastructure including schools, parks and green spaces, being
built, together with new housing, employment and transport infrastructure. Key
projects within the Tsuen Wan Road corridor identified in Section 8.1715 include:
·
MTR West Rail
·
Tsuen Wan West Rail Station
·
MTR residential development above tunnel
at TW5, TW6, TW7
·
Upgrading of Tsuen Wan Road
8.16.2
The contiguous settlements of Tsuen Wan
and Kwai Chung are located across a network of south-west aligned valleys and
ridges which form the convergence of the Kam Shan Country Park range to the
east and the Tai Mo Shan Country Park range to the west. A pronounced SW/NE aligned central ridge,
now accommodates the Kwai Shing Estate and terminates in the Chinese Cemetery
located on a ‘captured’ headland overlooking the Rambler Channel to the
west. The natural topography of the
area has been confused by a combination of platform creation, cut slopes which
now accommodates a large proportion of Tsuen Wan New Town, the closed Gin
Drinkers Bay landfill (Kwai Chung Park) and the extensive Kwai Chung Container
terminal.
8.16.3
The Tsuen Wan Road follows a NW/SE
alignment, parallel to the eastern edge of the Rambler Channel. The northern half between the junction with
the Castle Peak Road, in the north and Tsuen Tsing Interchange, in the south,
is on elevated structure. The Tsuen Wan Road previously defined the western,
coastal extent of the new town, however, a combination of the MTR West Rail
development will inbed the upgraded road within the urban area. The southern half of the Tsuen Wan Road between
the Tsuen Tsing Interchange and Kwai Tsing Road is in cutting as it crosses the
Chinese Cemetery/Kwai Shing Estate spur, reverting to a low embankment to the
east of Kwai Chung Park before transferring to structure at the Kwai Tsing
Interchange.
8.16.4
The four interchanges along Tsuen Wan RaodRoad at:
·
Castle Peak Road;
·
Tai Chung Road;
·
Tsuen Tsing Road; and
·
Kwai Tsing Road
8.16.5
Are all grade separated junctions with
associated highway structures, street furniture and well established and
maintained amenity planting to traffic islands, dividers and verges.
8.16.6
The prominent undersides, parapets and support
columns of the elevated section through Tsuen Wan are fully integrated with
matching curved profiles and all services hidden within the smooth textured
concrete structure. Staining of the
concrete surface has, however, occurred in places and the undersides of the
viaduct as it passes over Tsuen Wan Park has been painted beige to reflect more
light and present a more finished appearance.
8.16.7
The prominent undersides, parapets and support
columns of the elevated section through Tsuen Wan are fully integrated with
matching curved profiles and all services hidden within the smooth textured
concrete structure. Staining of the
concrete surface has, however, occurred in places and the undersides of the
viaduct as it passes over Tsuen Wan Park has been painted beige to reflect more
light and present a more finished appearance.
8.16.8
Whilst Section 8.1715 has described the
zoned land use for each Planning Area through which the Road passes, the
following description summarises the pattern of existing use.
8.16.9
Tsuen Wan Road currently links the two
principal areas of intense industrial use at Chai Wan Kok in the north and
those areas to the west of Yeung Uk Road and Kwai Fok Road to the south (Industrial
buildings along Tsuen Wan Road).
However, the expansion of Tsuen Wan has resulted in a number of large scale
residential developments of previously industrial lots on the coast including
Bayview Gardens, Belvedere Gardens, The Panorama, Serenade Cove, Waterside
Plaza and Riviera Gardens.
8.16.10 Between
there two areas of mixed industrial/residential development the Road passes to
the west of Tsuen Wan town centre. Land
uses, which adjoin
the road from north to south comprise the Clague Garden Estate, the Tsuen Wan
Transport Complex and Tsuen Wan Park (see Figure 8.4a). To the west
of the Tsuen Wan Road, the Tsuen Wan West Rail Station and its adjacent areas
along Tsuen Wan Road.
8.16.11 South
of Tsuen Wan Road, however, away from the coastline, the Road is lined by a
series of large industrial units of varying age. The only exceptions being the unsightly, chunam covered cut
slopes and container storage area to the southwest of the Tsuen Tsing Interchange
and the wooded flanks of the restored Gin Drinkers Bay landfill to the
northwest of the Kwai Tsing Interchange.
8.16.12 The
road corridor through Tsuen Wan contains a number of areas of established vegetation (See Tree Survey).
These may be summarised as follows:
·
At the high level interchange with the
Castle Peak Road the road corridor is flanked by a series of south east facing cut
slopes upon which semi-indigenous scrub woodland has become established. These slopes formare dominated with a group of Macaranga
tanarius ranging at 5m high and 4-5m spread in average, and also is be together
with the few of Ficus religiosa at8m high and 6m spread and Ficus benjamina at 6m
high and 9m spread, hence it forms a
visually important green “backdrop” to the urban area;
·
Areas of recently established ornamental
planting such as Bauninia blakeana, Cinnamomum burmannii,
Melaleuca leucadendron and Spathodea campanulata, and with their size ranging
from 5-7m high and spreading in 5-8m wide are located beneath and
adjoining the road viaduct between the Castle Peak Road Interchange and Tai
Chung Road;
·
The Clague Garden Estate is currently
partially screened from the elevated road by a large mound planted with semi
mature eucalyptus and casuarinas, as well as some feature tree species like
Casuarinn equiestifolia with the size ranging from 6-9m high and 3-4m spread,
Cinnamonum camphors at 9m high and 8m spread, Ficus virens var. sublanceolata at
6m high and 4m spread, Syzyginm jambos at 4m high and 3m spread and Melaleuca
leucadendron at7m high and 3m spread etc;
·
Tsuen Wan Park is similarly well
established with casuarina and other tree species, Bauhinia variegate Linn (4m
high and 2.5m spread); Casuarinn equiestifolia (7m high and 6m spread; or some
old mature above 10m high and 5m spread in sizes for examples, Cinnamonum
camphora (6-9m high and 6m spread), Elaecarpus hainanensis (6m high and 6m
spread) and Michelia alha DC (5-15m high and 3-5m spread),
adjoining the viaduct, filtering views of the structure and passing high sided
vehicles;
·
At the Tsuen Tsing Interchange
substantial areas of ornamental planting such as Caroyta ochlandra (30m
high and 3m spread), Ficus hispida (20m high and 3m spread) and Livistonia
chinensis (30m high and 3m spread) on traffic island and
indigenous scrub woodland on adjoining cut and fill slopes assist in
assimilating the grade separated interchange.
·
To the south of the Tsuen Tsing
Interchange the road returns to ground level and is flanked by an intermittent
thin belt of established casuarinas and also with feature trees like Ficus hispida (4m
high and 3m spread), Koelreuteria bipinnata (2m high and 1m spread) and
Macaranga tanarius (7m high and 4m spread) on
the cut and fill slopes between the factory units and the carriageway.
·
The most prominent feature is, however,
formed by the wooded flanks of the Gin Drinkers Bay landfill. The tree species found there
include Acacia confusa, Delonix regia,
Leucaena leucocephala and Corida dichotoma.
·
Whilst the manicured ornamental planting
associated with the Kwai Tsing Interchange provides a sharply contrasting
landscape character. Tree species
there include Roystonea regia (5.5m high and 2.5-3 spread), Syagrus
romanzoffiana (4m high and 2.5 spread) and Melaleuca leucadendron (9m high and
4-5 spread).
8.16.13 Key
eyesores adjoining the Tsuen Wan Road comprise:
·
The residual ‘old style’ go down block
facing Kwai Chung Park off Kwai Hei Street;
·
The chunam faced slopes adjoining the
Chinese Cemetery.
8.16.14 Positive
landscape features include:
·
The wooded slopes of Kwai Chung Park;
·
Ornamental planting at road intersections;
·
Tree planting to cut and fill slopes;
·
Tsuen Wan Park;
·
The vegetated hill slopes above Castle
Peak Road;
·
Views over the Rambler Channel;
·
Mature planting to the Clague Garden
Estate.
8.1.1
Sections
8.17
and 8.18
outline those known future developments along the
route corridor, which are likely to take place during the period 2011-2015. The
Tsuen Wan West Station Property Development Study indicates the nature and
extent of these developments through Tsuen Wan. The principle development which
will materially alter the urban landscape of the route corridor comprise the
MTR related residential towers at sites TW5, TW6, and TW7, the extension of
Tsuen Wan Park beneath the Tsuen Wan Road.
8.1.1
The southern section of the
upgraded road through Kwai Chung adjoins the visually prominent Planning Area
26. This area is currently undeveloped and underpassed by the MTR-West Rail.
Zoned for industrial use, however, this area is likely to be built out during
the period of the upgraded roads construction.
8.1.1
Within Planning Area 38 there
are also a number of ‘gap’ sites adjoining the road which are likely to be
developed for industrial purposes. Whilst Planning Area 37 – Kwai Chung Park
will be opened to the public before year 2009, increasing the number of
sensitive visual receptors overlooking the Tsuen Wan Raod and accessing the
park via the Kwai Tsung Road footbridge.
8.1.1
Figure 8.4a defines a
Primary Zone of Visual Influence (ZVI) for the upgraded road, within which
views of the road and its passing traffic may be secured.
8.1.1
The Tsuen
Wan (northern) section of the road corridor is characterised by open expansive
views across the Rambler Channel from Tsing Yi island to the west and a tightly
constrained visual corridor to the east against the urban edge of Tsuen Wan
town centre.
8.1.1
The Kwai
Chung (southern) section is, in contrast, visually confined by the built form
(industrial units) which line both sides of the road corridor.
8.1.1
Key viewpoints of the upgraded
road will be secured from: the pedestrian overbridges at Kwai Tsing Road and
Kwai Fuk Road; Residents of Waterside Plaza; residents of Riviera Plaza; new
residents of the proposed housing at sites TW5, TW6 and TW7; residents of the
Clague Garden Estate; residents of Skyline Plaza; visitors to Tsuen Wan Park;
residents located along the Castle Peak Road; children and staff attending the
Salvation Army Tsuen Wan Nursery.
8.1.1
The principal views for
motorists from the upgraded road will be from the northern elevated section
where glimpses between new residential blocks (TW 5, 6 and 7) across the
Rambler Channel to Tsing Yi Island and the Bridge.
8.17.1
This area of, largely, revegetated cut
hill slopes forms a green backdrop to western Tsuen Wan and an open, rural focal view for
motorists travelling north on the elevated road. The area is of sensitivity to the potential loss of established
vegetation as a consequence of its visual prominence.it is found with some local
village houses and its adjacent areas some small patches of agriculture
lands. Such area is featured with
Orchard trees and some individuals of Camellia japonica around the village
areas. Besides, plantation woodlands
at northward of Tuen Mun Road that is featured with Acacia Confusa and also,
the shrub land that is featured with Miscanthus sinensis on upper catchment
channel are found around the Tai Mo Shan Hill Slopes. However, these ornamental plants are not rare and are not protected
of Endangered Species of Animals and Plants Ordinance (Cap.586). This landscape
resource will remain of low sensitivity to further landscape change
since it is a very typical landscape feature in Hong Kong.
8.17.2
The Rambler Channel between the Chinese
Cemetery and the Castle Peak Road coast road currently forms Tsuen Wan
Bay. This coastal character area is featured with open space
and promenade area, where will remain of highlow sensitivity
to further landscape change.
8.17.3
Existing trees are found along the Tsuen Wan Road
including trees like Livistonia chinensis (3-5m height and 3m spread and
Phoenix rebelenii (2-4m height and 1.5-3m spread); other some mature trees like
Ficus benjamina (8-11m height and 8-10m spread); and other scattered trees like
Syzygium jambos (6-12m height, 3-6m spread), Spathosomedea campanulata (4-8m
height, 2-4m spread), Winchia calophylla (10-11m height, 4-6m spread) and
Bombax malabarium (6.5-12m height, 2-4m spread)
These trees underneath or
adjacent to the revised scheme alignment are typical urban landscaping feature
in Hong Kong, it will remain of low Sensitivity to further development.
8.1.1Figure 8.3 defines 3 main areas of
cohesive urban landscape character, which either intrude into or adjoin the
roads visual corridor. Corresponding
on site photos of the various landscape character areas are provided in Figure 8.3a.
8.18.1
Villages such as Pun
Shan Tsuen, Yau Kom Tau Village in this area locating at, largely, revegatated
cut hill slopes forms a green backdrop to western Tsuen Wan and an open, rural
focal view for motorists travellingtraveling north on the elevated road. The area is of low sensitivity to the potential
loss of established vegetation as a consequence of its visual prominence LCA 1 has a low
sensitivity to landscape change since it is such a typical landscape character
in Hong Kong.
8.18.2
This area of high-rise
residential blocks has progressively replaced the first generation industrial
go-downs, which characterisedcharacterized this coastal strip. LCA 2 has a
mediumlow sensitivity to
landscape change as a consequence of its residential use.
8.18.3
Future intensive
redevelopment of this corridor for residential purposes (TW5, 6 and 7) will
transform the character of this area whose sensitivity to further change is low.
8.18.4
This mixed use area is
currently undergoing extensive change as first generation new town development
is progressively redeveloped to a range of uses including retail, residential
and commercial. This developing landscape
remains of high sensitivity to further
change as a consequence of its strategic importance.
8.18.5
This well established
residential estate faces the elevated road but is currently well screened at
low level by an existing tree planted mound. The three residential tower
blocks, however, directly overlook the road corridor. The area includes a
nursery school and is of high
sensitivity to change.
8.18.6
The Riviera Gardens will
be separated from the upgraded road by the TW7 residential development and will
not, therefore, be directly affected by the works. Thus, it remains a low sensitivity to
change.
8.18.7
This area of mixed age
industrial units forms a dense cluster of blocks at the northern end of the
Tsuen Wan Road. The presence of the new
Chai Wan Kok Ventilation Building and the adjoining two industrial units (Kong
Nam Industrial Building) effectively extends the Chai Wan Kok Industrial Area
across the road at its junction with the Tuen Mun Road. This LCA is of low landscape sensitivity given its dense, industrial character.
8.18.8
This area of industry
extends from Tsuen Wan Park in the north to the Kwai Tsing Interchange in the
south along the road corridor. It is characterisedcharacterized by large
multi-story factory units with only a thin ribbon of roadside trees located on
residual embankments and cutting sides.
This vegetation is of considerable importance in softening the view from
the road and the area, is therefore, of medium
sensitivity to landscape change.
Others
8.18.9
The elevated section of
the Tsuen Wan Road currently defines the western edge of the Town Park. With the development of TW5 (Bayside) and
TW6 the park will be extended beneath the flyover to link up with the new
waterfront creating a direct pedestrian linkage between the town centre and the
Ramble Channel. The park is of high landscape sensitivity.
8.18.10
The well wooded, north
east facing flank of the restored landfill defines the southern edge of the
road and is of high landscape
sensitivity to change.
8.18.11
Similarly the Chinese
Cemetery is physically separated from the road corridor by LCA 12the Tsuen Tsing Interchange,
it will not, therefore, be directly affected by the works., and is of low
sensitivity to change.
8.18.12
This complex area
contains a wide diversity of urban landscapes, which surround this prominent
grade separated interchange, which is of low
sensitivity to landscape change.
8.1.1
Should the proposed upgrading
of the Tsuen Wan Road not proceed the baseline landscape of the route corridor,
as described above, is unlikely to materially change, beyond the continued
maturation of the existing roadside vegetation and the planting within Tsuen
Wan Park and Clague Gardens.
8.1.1
Visually, however, the
increasing congestion on the unimproved road will progressively intensify the
visual effect upon those sensitive receptors who overlook the road, eg. local
residents.
8.19.1
Sections
8.8 to 8.1213
of this assessment outline the assessment method for landscape and visual
impacts. The following sections,
therefore, seek to identify in a concise manner the principle effects of the
upgraded roads construction and operation upon the landscape of Tsuen Wan and
upon those sensitive visual receptors, who overlook the road corridor.
Sources of Impact
8.19.2
The construction of the upgraded road
will exacerbate the landscape and visual effects of the Tsuen Wan Road’s normal
operation by virtue of:
·
The presence of construction sites and
stock piles, whose location is undefined;
·
Intensified ‘visual clutter’ associated
with construction process’s eg. site hoardings, formwork and plant;
·
Intensified traffic movements associated
with construction traffic;
·
Intensified traffic congestion arising
from temporary traffic management schemes;
·
The regrading of cut and fill slopes;
·
Site clearance including the felling of
mature trees and other planting;
·
The presence of temporary haul roads; and
·
Construction activity in general.s; and
·
Construction activity in general.
8.19.3
Whereas the operation of the upgraded
road will intensify landscape and visual effects as a consequence of:
·
The increased width of the highway;
·
Loss of existing roadside planting;
·
Increased areas of shade beneath
structures; and
·
3 lanes of passing traffic in each
direction.; and
·
Installation of noise barriers/enclosures.
8.20.1
The
revised scheme alignment in the vicinity of the junction with Tuen Mun Road
will not require the regrading of the
vegetated lower, Tai Mo Shan Hill Slopes, resulting in slight to
insignificant construction, day 1 operation thus it will involve a
negligible magnitude of change and operationalresult in an irrespective
landscape effect, thus
resulting in an irrespective landscape effect.
8.20.2
The construction and
operation of the upgraded Tsuen Wan Road will not directly impact upon the open
expanse of the Rambler Channel. , it involves a negligible
magnitude of change and results in an irrespective landscape effect. Thus, it
results in an irrespective landscape effect.
8.20.3
Existing tree planting along the revised scheme
alignment that such landscape resources are typically found
in Hong Kong and used up as part of the open space and street feature and it is
also found along the slope, like at the Tsuen Tsing
Interchange and along the Industrial buildings adjacent to Tsuen Wan Road
respectively. However, such plant includes only a small proportion among the
total numbers of vegetation (see Figure 8.3 for details and Section 8.17.3 for
tree species). Thus, its
magnitude is intermediate
and results in an acceptable landscape
significance.
8.21.1
The nature landscape of
this little village area is not directly affected by the upgrading of the
TsuenWan Road. The revised scheme alignment in the vicinity of the junction
with Tuen Mun Road will not require the regradingregarding of the
vegetated lower, Tai Mo Shan Hill Slopes, resulting in slight to
insignificant construction, day 1 operation and operational landscape effectit will involve a small magnitude
impact and results in an acceptable
landscape significance.
8.21.2
The urban landscape of
this sensitive residential area is not directly affected by the upgrading of
the Tsuen Wan Road. However, such area involves a small
magnitude impact and results in an acceptable landscape significance.
8.21.3
The landscape effects of
the proposed road upgrading upon the Tsuen Wan Waterfront are limited by virtue
of the absence of existing features along this coastal area, with the exception
of six semi mature trees,
which adjoin Hoi Hing Road. The
waterfront is of low sensitivity to
landscape change whilst the road upgrading will involve a mediumintermediate
magnitude impact, resulting in an acceptable
landscape effect.significance. It should, however, be noted that the development of the Tsuen
Wan Waterfront for mixed use, including the MTR residential development of TW5
and TW7 will fundamentally change the existing open character of this extensive
character area (see Sections 8.16.4 and 8.16.5)...
8.21.4
The Tsuen Wan Town
Centre character area abuts the existing road in the vicinity of the Tsuen Wan
Transport Complex. This complex is in
the process of phased demolition in order to make way for the eastern half of
the MTR TW5 Cityside residential development.
The TW5 redevelopment has been designed in anticipation of the road
widening and a combination of the two developments will positively enhance the
landscape character of this key central area.
Their
cumulative effect is, therefore, considered beneficial.The magnitude impact
is therefore intermediate and results in an acceptable with
mitigation measures landscape significance during
construction; an acceptable landscape significance
both in day 1 and by year 10 of
Operation respectively.
8.21.5
This mature residential
estate includes 3 tower blocks, a commercial complex and nursery school
clustered around a central landscape garden.
A substantial planted screen bund currently filters views of the
elevated road and its passing traffic from the garden and the lower floors of
the residential blocks. Construction of
the widened road will result in a highlarge magnitude impact to this high
sensitivity area and necessitate the partial removal of the wooded screen mound
in order to accommodate an access/service road. The It results in acceptablesubstantial
impact significance before mitigation. And the removal of the outside face of
the screen mound and its associated mature trees will result in an acceptable with mitigation measures during
construction, an acceptable long term, operational landscape effect. in day 1 and by year 10 Operation respectively. These
measures to include the construction of a wall to retain the residual mound and
its vegetation, the protection of planting to be retained during construction
and the provision of additional evergreen, large specification trees (eg.
casuarinas) interplanted on the inside face and top of the screen mound to
reinforce the filtration of views from the housing and school.
8.21.6
The existing Riviera
Gardens will be separated from the widened road by the proposed MTR TW7
residential development. This ‘buffer’ development means that the Riviera
Gardens LCA will not be directly affected by the Scheme. Thus, its magnitude impact is
small and will result in an acceptable with mitigation
measures significance during construction, and then an acceptable landscape significance
both in day 1 and by year 10 of Operation.
8.21.7
This industrial area is of low landscape
sensitivity. The widening of the
elevated road to accommodate an additional lane to the east of the existing
road will, however, enclose the northern end of Hoi Shing Road beneath road
structure resulting in a loss of natural light at street level, a loss of
openness, an intensification of urban clutter and the temporary loss of
recently established amenity planting, resulting in a highan intermediate magnitude
of construction effect.
An intensification of replacement
roadside planting protected by raised/profiled granite block planters and the
screening of the proposed parking areas beneath the structure by curved feature
granite block walls will, however, mitigate the landscape effect to the Chai
Wan Kok Industrial Area to an acceptable
level in Day 1 and then a
beneficial level by Year 10 of Operation.
8.21.8
This extensive area of
large industrial buildings extends from south of Tsuen Wan Park to the Kwai
Tsing Interchange along the eastern road corridor. ,
resulting in a intermediate magnitude
of construction effect.
The widening works will
necessitate the removal of the existing roadside belt of casuarinas, which
currently provide the only visual relief to motorists passing through this
uncompromising urban corridor. This unacceptable
construction impact will progressively reduce to an acceptable with mitigation measures level by Year 10 (ie.
2025)Day 1
of Operation, however, as replacement planting progressively matures, resulting in a beneficial
landscape effect in Year 10 of Operation.
8.21.9
The Such local district park will
be directly impacted, its magnitude of change involve will be large.
Hence, the widening of the elevated road through Tsuen Wan Park will also
result in unacceptable construction
and short term effects upon the park as a consequence of the intrusion of
construction activities and the widened elevated structure and the temporary loss of existing established features including,
semi-mature trees, shrubberies, areas of hard landscape and other park features, which such loss is in term
of the pile construction along the road structure.
8.21.10
However, the cumulative, long term
operational effect of the parks extension beneath Tsuen Wan Road to join up
with the new waterfront promenade and the adjoining TW5 and TW6 developments
will reduce the effect upon this landscape character area to an unacceptable level during construction and
an acceptable with mitigation measures level.and an acceptable landscape significance
in day 1 and by year 10 of Operation respectively.
8.21.11
Construction of the
widened slip road and carriageway may impact upon the wooded toe of the Kwai
Chung Park side slopes. the
magnitude of change considers as large. This effect is likely to
be marginal in terms of the loss of existing roadside trees and capable of long
term mitigation through replacement planting if necessary. The landscape impact of the Scheme is,
therefore, considered acceptable upon
the park. both in day 1 and by Year 10 of Operation.
8.1.1
The Chinese
Cemetery, although intermittently visible from the existing and proposed road,
is not directly affected by the Schemes construction or operation.
8.21.12 Though
such landscape character has no direct affected by the works, its magnitude of
change is negligible and results in an irrespective landscape effect.
8.21.13
The grade separated
Tsuen Tsing Interchange currently benefits from a variety of well -established planting
located on traffic islands, verges and meridians. Road widening will required the removal of
areas of this planting. The
magnitude of change is small. However, new planting and the
replacement if existing chunam covered slopes with regradedregarded and planting
areas will reduce the effect to an acceptable
level in day 1 and a beneficial
significance by Year 10 of Operation.
8.22.1
SectionsFigure 8.19 and 8.20 of this report identified4a defines a Primary Zone of Visual Influence
(ZVI) for the upgraded
road, within which views of the road and its passing traffic may be secured.
8.22.2
The Tsuen Wan (northern) section of the road
corridor is characterised by open expansive views across the Rambler Channel
from Tsing Yi island to the west and a tightly constrained visual corridor to
the east against the urban edge of Tsuen Wan town centre.
8.22.3
The Kwai Chung (southern) section is, in contrast,
visually confined by the built form (industrial units) which line both sides of
the road corridor.
8.22.4
Key viewpoints of the upgraded road will be secured
from: the pedestrian overbridges at Kwai Tsing Road and Kwai Fuk Road;
Residents of Waterside Plaza; residents of Riviera Plaza; new residents of the
proposed housing at sites TW5, TW6 and TW7; residents of the Clague Garden
Estate; residents of Skyline Plaza; visitors to Tsuen Wan Park; residents
located along the Castle Peak Road; children and staff attending the Salvation
Army Tsuen Wan Nursery.
8.22.5
The principal views for motorists from the upgraded
road will be from the northern elevated section where glimpses between new
residential blocks (TW 5, 6 and 7) across the Rambler Channel to Tsing Yi
Island and the Bridge.
8.22.6
Such Primary Zone of Visual Influence (ZVI) and
key sensitive visual receptors for the proposed Scheme. This section considers the effects of the
upgraded roads construction and operation upon each of these receptor groups
views and identifies mitigation proposals where necessary.
8.22.7
Visual receptors within the Primary ZVI
have been categorised as follows:
High to Medium Sensitivity
·
Local Residents
·
Parks Users
·
School Children and teachers
·
Local Drivers
Medium to Low
Sensitivity
·
Footpath Users
·
Footbridge Users
·
Local workers
·
Passing motorists
8.23.1
Residents (Pun Shan
Tsuen & Yau Kom Tau Village) living at and few of the hikers at Tai Mo Shan
Hill Slopes, can have open views of the upgraded roads construction and
operation across Tsuen Wan Bay. The mass hill slope vegetation will obscure the
view and indeed, the existing and the future upgraded road has been the
habitants and hiker’s every day frequent view so it will only remain a small
magnitude of impact and cause slight to insignificantan acceptable
construction, day 1 operation and operationalby Year 10 operation landscape effect.
8.23.2
Residents of those tower
blocks which line the south side of Castle Peak Road including Belvedere
Gardens Phase III, Serenade Cove and Bayview Gardens will have open views of
the upgraded roads construction and operation across Tsuen Wan Bay. The widened elevated road, however, will
form a relatively minor component of the wider urban edge landscape whilst the
MTR TW5 development for a mixture of uses including high rise housing, will
obscure sections of the new road from view.
8.23.3
To the north of the
Castle Peak Road residents of The Panorama and Belvedere Gardens Phases 1 and 2
and those residents in tower blocks on the hillside east of the Tuen Mun Road
will obtain medium distance overviews of the relatively minor works required to
merge the existing Tuen Mun Road with the widened Tsuen Wan Road. These works will not involve major cutting
into the wooded hillside.
8.23.4
Notwithstanding the
sensitivity of residents to change in their views, the construction and
operation of the widened road will involve a relatively lowsmall magnitude of
change resulting in an acceptable with mitigation measures in day 1 and by year 10 of
visual effect
respectively.
8.23.5
Residents of the four
tower blocks which form Waterside Plaza currently directly overlook the road in
the vicinity of the Tsuen Tsing Interchange. The magnitude of change considers as Intermediate.
Whilst the proposed widening will bring passing traffic closer to these
sensitive visual receptors the construction of the 5 residential tower blocks
of the MTR TW7 over the tunnel corridor will obscure most views of the upgraded
road resulting in an acceptable with mitigation measures cumulative
visual effect. during construction.
8.23.6
Construction of the
upgraded road is currently scheduled for 2011-2015, whilst the completion year
for the MTR residential towers at sites TW5, would be 2015-2016, TW6 would be
2012 and TW7 would be 2012-2014.
8.23.7
Given that these
developments have been designed to accommodate the widened road and that new
residents will be aware of the upgraded roads proximity and construction
programme at the time of purchase, the visual effects of construction and
operation of the widened road are considered acceptable visual
effect both in day 1 and year 10 of Operation for new residents.
8.23.8
Residents of the single
tower block at Skyline Plaza and the twin towers above Tsuen Wan Plaza whilst
outside of the primary ZVI, have medium distance overviews of the road between
the existing Tsuen Wan Transport Complex and the newly constructed Nina Tower
complex. The magnitude of
impact is thus considered as small.
8.23.9
The proposed upgrading
of the elevated road will result in an
acceptable visual effect as a consequence of distance and the intervening
development whose cumulative screening effect will be enhanced by the
construction of the MTR TW5
(Cityside) residential towers.
8.23.10
Residents of this
established estate are in closest proximity to the road whilst the additional
elevated road section will intrude into the estates mature gardens resulting in
a loss of semi-mature trees which currently filter views of the road and its
passing traffic from ground level and lower residential floors. Thus, the magnitude of change
is intermediate.
8.23.11
The visual effect to the
residents of Clague Garden Estate during construction stage is, therefore,
considered substantialacceptable with mitigation measures. Whilst the long term operational effect will
progressively improve to moderate level as new reinforcement screen planting
matures, results in an acceptable
significance both in day 1 and by Year 1 of Operation.
8.23.12
Residents of the
extensive Riviera Gardens estate will incur medium distance overviews of the
upgraded roads construction and subsequent operation. These views will be seen, however, against the backdrop of Tsuen
Wan’s urban edge and will be further obscured by the construction of the intervening
MTR TW5 (Bayside), TW6 and TW7 residential
towers, thus is
considered as a small magnitude of change and resulting in an acceptable long term visual effect.
8.23.13 Some workers of the Chai Wan Kok Industrial Area incurs short distance
overviews of the upgraded roads construction and subsequent operation. These
views will be seen, however and as intermediate magnitude of change. However,
against the backdrop of the Tsuen Wan’s Rambler Channel and sea views and will
be further obscured by the construction of the greening element alone the road
expansion as mitigation measures, resulting in an slight and insignificant long
term visual effect. acceptable
significance in day 1 and beneficial significance by year 10 of
Operation.
8.23.14
Some workers working at the industrial buildings along Tsuen Wan Road incurs short distance overviews of the upgraded roads
construction and subsequent operation. These views will be seen, however and involves an intermediate
magnitude of change. However, against the backdrop of the Tsuen Wan’s
Rambler Channel and sea views and will be further obscured by the construction
of the greening element alone the road expansion as mitigation measures,
resulting in an slight and insignificant long term visual effectacceptable for both day 1 and year 10 of
Operation.
8.23.15
Tsuen Wan Park is an
extremely popular facility, well used by both local residents and others
accessing the adjacent town centre. It involves a large magnitude of change.
Construction of the additional elevated road lanes will result in onan unacceptable level of visual construction effect upon park
visitors. In the longer term, however,
ie. by Yearyear 10 of Operation
(2025) the cumulative effect of reinstatement works and the extension of the
park beneath the road structure to the waterfront promenade will result in a slightan acceptable
long term visual effect.
8.23.16
Magnitude of change is small. Construction
works are unlikely, however, to result in significant tree loss at the toe of
the adjoining park hillside, resulting in an acceptable visual effect upon park users.
8.23.17 Visitors
do not frequently go to the Chinese Cemetery schedule but only in regular
festivals. The Magnitude
of change considers as small. The proposed tree planting as screening at the hill slopes and
along the road expansion and its relative long distance away from the road,
resulting to an slightacceptable significance in day 1 and insignificant
long term visual effect. a
beneficial significance by year 10 of Operation.
8.23.18
Pedestrians passing in
the vicinity of the road corridor during construction will experience a range
of visual effects, however, manythe Magnitude of change will be intermediate,
thus, it involves an acceptable significance in Day1 and beneficial
significance by Year 10 of Operation. Many will experience exacerbated
visual intrusion as a consequence of construction activities and the removal of
localisedlocalized amenity
planting from road intersections and the road margins, resulting in an
acceptable with mitigation effect. By in day1 of Operation and by
year 10 of Operation, however, the screening of the spaces beneath the viaduct
structure with a combination of granite screen walls, raised planters and new
planting will positively improve the street level landscape resulting in a beneficial long term effect.
8.23.19
Pedestrians accessing
the Kwai Tsing Road and Kwai Fuk Road footbridges currently gain unobstructed
overviews north and south along the road.
These views benefit from the wooded flanks of Kwai Chung Park and the roadside
belts of casuarinas trees,
which soften the urban landscape and form a transition between the vertical
plane of the adjoining factory blocks and the horizontal plane of the road. The Magnitude of change will
be large. However, the number of sensitivity receivers is very few.
8.23.20
Road widening will
result in the removal of the casuarinas belts resulting in an acceptable with
mitigation construction effect. This
will progressively reduce to an acceptable
level in day 1 and beneficial
significance by Year 10 of Operation as replacement roadside planting
matures.
8.23.21
Children and teacher in the vicinity of the road corridor during construction will
experience a range of
visual effect and the Magnitude of change will be intermediate. It will
result in an unacceptable significance and incur an
acceptable withsome possible mitigation visual effect as a consequence of the loss of existing
established roadside planting in places and the visual intrusion of construction
activities and works.
8.23.22
By year 10 of operation,
however replacement planting to the road margins and at intersections will have
sufficiently matured to reduce the visual effect upon bypass users
to an unacceptable level. in day 1 Operation and an acceptable
with mitigation measures level by year 10 of Operation.
VSR 15 Passing Motorists – Local Road Network
8.23.23
Motorists accessing the
local road network in the vicinity of the road during construction will incur
an acceptable with mitigation measures visual effect as a consequence of the loss
of existing established roadside planting in places and the visual intrusion of
construction activities and works.
8.23.24
By Year 10 of operation,
however, this visual effect will have turned to a positively beneficialacceptable effect as
the unsightly areas beneath the viaduct are screened and enclosed by feature
granite walls and planting which will conceal a series of small car parks.
8.23.25
Motorists accessing the
Tsuen Wan Road during construction will incur the intensified visual activity
of construction works whilst the removal of existing roadside trees will
significantly downgrade the appearance of the road corridor resulting in an acceptable with mitigation visual
effect.
8.23.26
By Year 10 of Operation,
(2025), however, replacement planting to the road margins and at intersections
will have sufficiently matured to reduce the visual effect upon road users to
an acceptable level.
8.24.1
The assessment process has generated a
range of practical landscape proposals, which will effectively mitigate those
significant landscape and visual effects identified. These mitigation proposals include:
·
MM1 - Tree planting proposal including Tree Preservation
Scheme
The replacement of amenity planting lost
as a consequence of road widening and the remodeling of junctions. By proposing
a new planting theme, it aims to provide a comprehensive green system that the
amenity planting allows an enjoyable outdoor seating out area whilst tree and
shrub plant along Tsuen Wan Road allows a screening and pleasant effect to
connect up with its adjacent areas.
Tree Preservation proposal
involving minimization of tree felling and transplanting is also considered
accordingly.
·
MM2 – Provision of screen walls and planting
areas
The re-use of areas beneath the elevated
road deck as public sitting out area, screened by feature granite block walls
and amenity planting, that this feature is made of innovative, cost effective
and durable materials and pedestrians will feel pleasant to walk through and
stay in as a resting area.
·
MM3 – Feature finishes to structures and
floor paving
The provision of feature granite block
screen walls and raised planters around car parks and on traffic islands and
meridians is used to enhance the existing environment along Tsuen Wan Road.
·
MM4 – Provision of new recreational /
amenity facilities
Reinstatement of Tsuen Wan Park includes
the provision of new recreational and amenity facilities. Particularly the
existing plant inside the park and in future, in order to in cooperate with its
adjacent to the Tsuen Wan Road expansion, the adjustment of plant will be
proposed to provide a pleasant amenity and a close connection to the green
environment.
·
MM5 – Provision of noise barriers
The provision of a visual / acoustic
screen particularly the noise barriers adjacent to the Clague Garden Estate.
This should be achieved through the use of innovative form, recessive and muted
colors and tones, and through use of materials. And green plant such as colorful
shrubs and climbers is proposed to plant along part of the overall noise
enclosure structure. The design of the engineering structure thus aims to
minimize visual impact as far as possible and visually integrate as far as
possible into the landscape context.
·
The details of mitigation measures are
provided in Figure 8.16 5 to 8.19.
i) Design and Construction of the soft
works recommended at the above MMMMs 1-5
i) During the construction stages, soft landscape measures
should be used where appropriate, employing native plant species as fast as
practicable, to restore the green land cover and enhance the vegetated, urban
environment. This includes tree/ shrub planting and hydro-seeding in the
peripheral site area, footpath side, access road, park and open spaces.
ii)
During the operation stages, the newly
planted trees, shrubs and grassed areas are maintained throughout the
establishment perooidperiod at the intervals extablishedestablished in the soft
works specification, particularly in respect of the following:
- Regular grass cutting for reinstated areas
frequently to be established in the woftsoft works specification;
-
Firming up of trees after periods of
strong winds periods to be established in the soft works specification;
-
Regular checks for and eradication of
pests, fungal infections etc. frequently to be established in the soft works
specification;
-
Pruning of dead or broken branches
frequently to be established in the soft work specification;
-
Replacement of dead plants and resending
of failed areas of grass as early as possible during the planting seasons, i.e.
between March and September, although the optimum period is between April and
July, to ensure the landscape mitigation measures fulfil their design intention
-
The management and maintenance aurthoirityauthority will make
regular bimonthly inspections of the planted areas during the establishment
period to ensure the intended objectives of the landscape and visual mitigation
measures are achieved.
8.24.2
The widening proposals will require the
implementation of extensive noise attenuation measures and so it is proposed
that some 738m of noise enclosure and 2,183m of noise barrier are constructed
along a part of the alignment. The dimensions including height and length of
the proposed noise mitigation measure are given below.
Height (m) |
Length (m) |
5.5 +3.5 (cantilevered sections) |
2,183 |
Semi-enclosure |
477 |
Full-enclosure |
261 |
Total length of barrier |
2,921 |
8.24.3
These barriers have been identified
within the impact assessment as being an added source of visual impact. Depending on their location they may
introduce a high vertical element and visual barrier along sections of road,
with some barriers including 5.5m high vertical barriers with a 3.5m cantilever
at 45 degrees. On the bridges, they may
increase the depth of the profile of the road causing a slender road deck, when
viewed from distance, to become a visually heavy structure.
8.24.4
All barriers, including cantilever types,
will be based on a single design theme to create a single family of structures,
which will also be integrated with the engineering structures, avoiding
excessive visual clutter along the road.
All barriers are noise reflective type and can, therefore, be clear. The
barriers will comprise semi-transparent panels with a colour tint supported by
posts coloured in muted tones reflecting the local visual environment.
8.24.5
This strategy in
tandem with the proposed soft landscape mitigation measures will alleviate some
of the potential overall visual intrusion which barriers may cause. In a majority of locations the barriers will
be required along the elevated bridge structure. At these locations, planting along the bridge structure will be
used to screen the barriers (See Figures 8.16 and 8.18).
Moreover, greening panel has been taken into design consideration for mitigate
the visual impact of noise barriers. All barriers required will be submitted to
ACABAS for comment during the detail design stages.
8.24.6
Alternative ‘soft’
noise mitigation measures, such as earth bunds have been considered. However,
as the road is designed on elevated structure, and the works boundary has been
limited to minimise impact, this approach is not a feasible option. The use of
earth bunds to an appropriate height for noise mitigation would require extensive
additional land take along side the road and hence result in additional
landscape impacts.
8.24.7
The funding and
implementation of the proposed mitigation measures will be the responsibility
of the Civil Engineering and Development Department. Once the day 1 operation
started, the relevant departments, such as HyD, LCSD etc. will be the
responsible for the management and maintenance of the proposed mitigation
measures. Conceptual landscape layout and photomontages of the
mitigation measures are provided in Figure
8.10a to 8.10d10e.
8.25.1
Figure 8.11
and 8.12 demonstrate how the implementation of effective landscape
mitigation measures (see Figures 8.85
to 8.9) will progressively reduce both long term landscape and visual
impacts to an acceptable (with mitigation) or beneficial level.
8.25.2
The only exception identified being the
visual effect upon the children and staff at Tsuen Wan Salvation Army Nursery
who will incur a significantan unacceptable
residual visual effect due to the proximity of the widened road and
notwithstanding the provision of a substantial visual/acoustic screen above the
road parapet.
8.26.1
It is recommended that an Environmental
Monitoring and Audit Manual and Implementation Schedule be prepared for the Tsuen
Wan Road Upgrading. This would include,
inter alia, recommendations on tree protection measures during construction, a
short term plant establishment plan and a long term Landscape Management Plan. A programme of site inspections, both during
construction and operation will be identified.
8.27.1
The construction and operation of the
Tsuen Wan Road Upgrading will result in a wide range of landscape and visual
effects along the route corridor.
8.27.2
Visual effects are particularly prominent
along the northern, elevated section where the road is overlooked by a number
of residential tower blocks. The
widened road also passes extremely close to a school and through Tsuen Wan Park
causing significant visual and landscape effects.
8.27.3
Landscape effects along the southern,
ground level section, are more pronounced, with the carriageway widening works
resulting in the loss of the established belts of casuarina trees on either
side of the road.
8.27.4
Notwithstanding these significant
construction and short term effects the implementation of those landscape
mitigation works identified will progressively reduce virtually all effects to
an acceptable level by Year 10 of Operation.
The only long term, significant residual effect identified being upon
the pupils and staff of the Tsuen Wan Salvation Army School, whose school
building and playground will be overshadowed by the proximity and form of the
elevated widened road, notwithstanding the provision of a visual/acoustic
barrier.