This section deals with the key
landscape and visual impact issues of the proposed 3 x 132kV electricity supply
circuits leading from Pui O Substation at Lantau Island south to Cheung Chau
Substations (hereafter described as
“the project”). The purpose of this section is to:
· identify the relevant legislation and guidelines to be used in the landscape and visual impact assessment (LVIA);
· define the LVIA methodology;
·
conduct
a LVIA;
·
evaluate
the significance of landscape and visual impacts:
·
recommendation on mitigation measures so as to minimize environmental disturbance
and nuisance during c onstruction
and operation of the project;
· evaluate the residual landscape and visual impacts with mitigation measures implemented.
The methodology of the LVIA will be based on Annexes 10 and 18 in the Hong Kong SAR Government's Technical Memorandum on the Environmental Impact Assessment Process (EIAO-TM) under the EIA Ordinance (Cap.499, S16), entitled "Criteria for Evaluating Visual and Landscape Impact" and "Guidelines for Landscape and Visual Impact Assessment", respectively.
The main components of the LVIA were as follows:
· baseline study of landscape and visual resources including a review of planning and development control framework;
· landscape impact assessment during construction and operation;
· visual impact assessment during construction and operation;
·
recommendations for landscape and visual mitigation
measures for both
construction and operation stage.
· assessment of residual impact and conclusion on the acceptability of the Project.
Figure 8.1 illustrates the Landscape and Visual Impact methodology stages.
Project
Description
The project description
explains and identifies the major components of the proposed project. It
describes both the construction and operational aspects of the project.
Baseline
Landscape and Visual Resource Study
The baseline study identified and examined the existing landscape and visual resources within the study area. Under the study brief, the study area defined for the landscape impact assessment is approximately 300 metres out from the proposed works site boundary and the assessment area for the visual impact assessment defined by an visual envelope.
Landscape resources considered included
topography, woodland types, other vegetation, built forms, settlement patterns,
land use, scenic spots and details of local streetscapes. The baseline study describes the landscape
resources by identifying broadly homogenous landscape units (LCUs) of a similar
character. The landscape character was
rated low, medium or high depending not only on the quality of elements present
but also to its sensitivity to change and its importance at a local, district,
regional or international level.
Visual resources considered were
typical viewpoints, location and direction of views towards the project. An visual
envelope (refer to Figure 8.710) was
established which approximately defined the extent of visual influence of the
project and, therefore, of the potential visual impacts. Definition of the
extent of the viewshed was based on desktop study and site investigation. The visual
envelop/viewshed is generally formed by natural/man made features such as
ridgeline or building blocks. Sensitive visual receivers (SVRs) identified in this report
are “representative” in that individuals or groups (SRs) that have a similar sensitivity to
changes in the visual and landscape
environment are grouped together within a single SVR that can represent the whole group. who would
be present at typical viewpoints and likely to be affected by the Project were
identified within the viewshed. Sensitive visual receivers (SVRs)
are individuals or groups of who are sensitive to changes in the visual
environment. The Hong Kong Planning
Standards & Guidelines, Chapter 9 Environment, defines sensitive users as
“land uses which, by virtue of the nature of the activities thereon….are
susceptible to the influence of residual or physical changes generated by
polluting uses”.
Review of Planning and Development Control Framework
The next stage was a review of
the planning and development control framework. Under Annex 18 of the TM of
EIAO, landscape related zonings on the Outline Zoning Plan (OZP) was mapped and
analysed to provide an insight to the future outlook of the area affected and
the way the Project would fit into its wider context. Conflicts with the statuary town plans were highlighted and
appropriate follow-up action was recommended as required from the study brief. The review includes statutory and non-statuary documents are the followings:
·
South
West New Territories Development Strategy Review
·
The
Draft South Lantau Coast Outline Zoning Plan (OZP) No. S/SLC/11
·
The
Cheung Chau South Layout Plan L/I-CCS/2C
·
The
Cheung Chau Central Layout Plan L/I-CCC/2
·
The Cheung Chau North L/I-CCN/IB
Landscape Impact Assessment
The following stage was to assess
impacts on the landscape and visual resources during construction and
operation. The impact assessments allow predictions to be made about the likely
levels and significance of landscape and visual impacts. The assessment of LANDSCAPE impacts will result from:
The overall landscape impact
is a product of the following:
· The landscape character and its quality;
· The sensitivity of the landscape in accommodating change;
· Source, nature and magnitude of impacts;
· The degree of change caused by the impacts to the existing landscape;
· Significance of the change in consideration of the local and regional areas and other developments;
· Cumulative effects with other proposals;
·
Identification of vegetation of significant value which
should be conserved.
The sensitivity / quality of the landscape will be assessed as follows:
· High: e.g. important components or landscape of particularly distinctive character susceptible to small changes;
· Medium: e.g. a landscape of moderately valued characteristics reasonably tolerant to change;
·
Low: e.g. a
relatively unimportant landscape, which is able to accommodate extensive
change.
The magnitude of change in the landscape is as follows:
· High – notable change in the landscape characteristics over an extensive area ranging to very intensive change over a more limited area;
· Moderate – moderate changes to a local area;
· Low –changes to components;
·
Negligible –
no perceptible changes.
The system for the assessment of landscape
impact is summarised in Figure 8.2.
The significance threshold of landscape impact is derived from the combined
analysis of the magnitude of change and the landscape’s quality and sensitivity
to change. A matrix (Figure 8.2) is
used to assess the level and range of impact from low to high in relation to sensitivity
of the landscape resource and the magnitude of change resulting from the
proposal. This analysis of the degree of landscape impact will apply
in the majority of situations, however in certain cases a deviation may occur
e.g. the impact may be so major that a significant impact may occur to a low
quality element.
Visual Impact Assessment
The assessment of potential VISUAL impacts will result from:
· The sensitivity of the viewer groups at SVR locations to change and visual intrusion;
· the magnitude of change to the visual baseline condition.
The sensitivity of viewer groups at SVR locations will be classified as follows:
·
High -
- the nature of the viewer groups expects a high degree of control over their immediate environment, (e.g. people residing in their homes); and
- The viewer groups are in proximity to the project; and
- The foreground and middleground cannot visually absorb the Project.
·
Medium -
- the nature of the viewer groups expects a high degree of control over their immediate environment, (e.g. people residing in their homes); but
- The viewer groups are not in proximity to the Project; and
- The foreground and middleground can partially absorb views of the Project.
·
Low -
- the nature of the viewer groups do not expect a high degree of control over their immediate environment, (e.g. people at their place of employment or temporarily in attendance at the SVR location); and
- People in transit (e.g. drivers and passengers in vehicles); and
The magnitude of change is classified as follows:
·
High -
- Prominent and permanent visual changes in the foreground, middleground or background where the project dominates the view;
- Permanent visual changes where the project contrasts conspicuously against the middleground and/or background;
- Temporary visual changes where the project dominates the foreground view.
·
Moderate -
- Permanent visual changes in the foreground or middleground where the project is prominent but does not dominate the view;
- Permanent visual changes where the project is discernible against background, but is not conspicuous.
- Temporary visual changes where the project dominates the middleground view.
·
Low -
- Permanent visual changes in the foreground, middleground or background where the project is present but not noticeable;
- Temporary visual changes where the project dominates the background view.
·
Negligible -
- No visual changes are apparent.
The system for the assessment of visual impact is summarised in Figure 8.3. The significance of visual impact is derived from the combined analysis of the magnitude of change and the visual receivers' sensitivity to change. A matrix (Figure 8.3) is used to assess the level and range of impact from low to high in relation to sensitivity of the visual receiver and the magnitude of change resulting from the proposal. The significance of visual impact is assessed for the construction phase and for the operation phase.
Recommendation for Mitigation Measures
Following impact assessment the next
stage is to assess and recommend mitigation measures. The identification of the landscape and visual impacts will
highlight those sources of conflict requiring design solutions or modifications
to reduce impacts, and if possible absorb the development and associated
activities into the surrounding landscape. These mitigation efforts will
consider factors such as:-
· Woodland, tree and shrub planting to new or disturbed slopes, amenity strips, highway reservations and adjacent to any proposed structures;
· Contouring of new slopes to blend with existing topography in a natural manner;
· Earth mounding and screening;
· Alternative site planning
· Alternative construction methodology and phasing
The above will result in the formation of landscape and visual mitigation proposals which will as far as possible help to alleviate previously identified impacts.
Residual Landscape and Visual Impacts
The final stage of the LVIA study is to assess the significance of the residual impacts of the study assuming landscape mitigation measures are incorporated into the design. The landscape and visual impacts were then classified into five levels of significance based on criteria in Annex 10 of the EIA-TM, as summarised below:
· The impact is beneficial if the project will complement the landscape and visual character of its setting, will follow the relevant planning objectives and will improve the overall and visual quality of the study area;
· The impact is acceptable if the assessment indicates that there will be no significant effects on the landscape, no significant visual effects caused by the appearance of the project, or no interference with key views;
· The impact is acceptable with mitigation measures if there will be some adverse effects, but these can be eliminated, reduced or offset to a large extent by specific measures;
· The impact is unacceptable if the adverse effects are considered too excessive and are unable to mitigate practically;
· 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.
The project and construction methodology is described in
detail in Section 2 of this EIA. For the purposes of this LVIA the project comprises
the following sections (1-5) and subsections (2a, 3a & 3b) as described in Table 8-1 below.
In brief the proposal is for a new 3 x
132kV electricity supply circuits from the existing Pui O Substation on south
Lantau Island, via Chi Ma Wan Peninsula via Adamasta Channel towards Cheung
Chau North and Cheung Chau South Substations.. Figure 8.4 & 8.5
indicates the alignment and overall construction of the underground cable. The
circuit proposal comprises underground sections on land and sea, as well as 1
tunnel portal (ventilation building) and 2
landfall areas. The
most significant above ground structure
within the proposal is the tunnel portal located at Pui O (refer to Table
8.1 section 2a).
The tunnel portal is an integrated building that comprises access as well as
ventilation systems for the tunnel.
The construction phase will require
the construction of cut and cover trenches, the boring of a tunnel and lying of
a submarine line. Construction will also require the formation of works areas (including a temporary working
platformreclaimed land) to allow access to the
construction sites for the tunnel portals. The operational phase will be
largely related to periodic maintenance of the cable of the underground cable. For the
purposes of this LVIA the project comprises the following sections (1-5) and
subsections (2a, 3a & 3b) as described in Table 8-1:
Table 8-1 Segmentation
of the Cable Alignment
Section |
Location |
Length |
Works Area |
Construction Method |
1 |
Pui O Substation to Pui O Beach |
approx. length
2350m |
along South
Lantau Road & Chi Ma Wan Road |
Open trench excavation method, 3 x 132kV circuits of underground cable
will be laid in trench not exceed 50m long at once time. |
2 |
Pui O Beach to Tai Long Wan east using
cable tunnel |
approx. length 3000m |
Pui O tunnel
portal (2a) & Tai Long Wan landfall area (2b) |
Tunnel Boring
Machine (TBM), 3 x 132kV circuits will be laid in a tunnel with 3m diameter. |
2a |
Pui O tunnel
portal |
|
Size: Tunnel Portal (with
ventilation system Cut slope area: 750m2
Height of Cut
slope: 23m (Crest 27 mPD Temporary
|
|
3 |
Tai Long Wan
to Cheung Chau Sai Tai Road using submarine cable |
approx. |
Submarine cable
laid in 5m x .75m precast concrete trough |
3 x 132kV circuits in submarine cables will be laid by direct burying
method and only one submarine cable will be laid during each operation. |
3a |
Tai Long Wan
landfall area |
|
Size: Tai Long Wan landfall area 2.4m by 3.4m Cut slope area: 700m2 Height of Cut
slope: 17m (Crest 49 mPD Temporary access: 350m2 |
Landfall area for submarine cable. Cut slope and temporary access for
delivery for the site work will be back filled and reinstated. Dredging may
be required at both landfalls when the water is too shallow. The temporary access |
3b |
Cheung Chau Sai Tai landfall area |
|
Size: 6m x 3m x 3m landing point
connected to precast concrete trough |
Landfall area for submarine cable. Dredging may be required at both
landfalls when the water is too shallow. |
4 |
Cheung Chau Sai Tai Road to Cheung Chau
South Station using underground cable |
approx |
|
Open trench excavation method, 2 x 132kV circuits of underground cable
will be laid in trench not exceed 50m once at once time.
|
5 |
Cheung Chau Sai Tai Road to Cheung Chau
North Station using underground cable |
approx. length 1250m |
|
Open trench
excavation method, 1 x 132kV circuits of underground cable will be laid in
trench not exceed 50m once at once time.
|
Possible lLandscape
and visual impact will arise from the from the following elements
of the proposed project:
· loss of existing trees and vegetation owing to construction activity associated with trenching and construction of Pui O Tunnel Portal and Tai Long Wan landfall area;
· Disturbance of rocky shore and sandy beach owing to construction activity associated with trenching and construction of Pui O Tunnel Portal and Tai Long Wan landfall area;
· Impacts on existing manmade promande owing to construction activity associated with trenching and construction of Cheung Chau Sai Tai landfall area;
· loss of scenic quality owing to the presence of built structures in a country park, coastal protection area and other rural landscapes;
· Temporary loss of ground floor view to the sea along Cheung Chau Promenade and Sai Tai Road;
The project area traverses a
complex range of landscape and visual resources comprising the rural townships
of Pui O and Cheung Chau and the Lantau South Country Park extending over Chi
Ma Wan Peninsula. Figures 8.6 and 8.7. The
landscape character ranges from Harbour and Beach coastal edge settlements
comprising predominantly 3 storey buildings to predominantly natural coastline
and wooded country park. Visual resources are concentrated at the settlements
of Pui O and Cheng Chau, but also include visitors to the Country Park and users
and passengers of vessels using the Adamasta Channel between Chi Ma Wan
Peninsula and Cheng Chau. To assist in identifying specific landscape impacts a
detailed tree survey has been undertaken for Pui O tunnel portal and Tai Long
Wan landfall area. The results of the tree survey are indicated in Appendix I.
The
study area was categorised into distinctive landscape character units (LCUs)
depending on presence and combination of landscape pattern, mass and scale of
buildings and structures, topography, and existing vegetation. An assessment has also been made of the
likely ability of each LCU to accommodate changes caused by the project. The results of landscape baseline study are
described in Table 8-2 and shown on Figures 8.6 8 and 8.9
Table 8-2 Summary of Landscape Character Units (LCUs)
Landscape
Character Unit |
Name |
Description |
Sensitivity
to Change |
LCU1 |
Mixed Village & Agricultural Uses |
Low-density village areas with a periphery of agricultural
land which is progressively being abandoned; three-storey village houses
interspersed by mature trees and fields; generally level to shallow sloping
land; easily accessible by roads and paths. |
Low |
LCU2 |
Township |
Medium-density village areas with commercial activities at
G/F, such as seafood restaurant, local shops and cafes, creating unique main
street character in island. |
Low |
LCU3 |
Community Facility |
Community and local commercial uses, such as market,
library, post office, clinic etc, two to six storeys buildings. |
Medium |
LCU4.1 |
Woodland |
Steep to gentle densely wooded slopes with mature
woodland; generally inaccessible to access by public except via existing
footpath network. Recreation areas, such as camp sites, rest garden, plaza in
sections 1 & 4. |
High |
LCU4.2 |
Recreation |
Publicly accessible recreation areas, such as camp sites,
rest garden and plaza |
High |
LCU5 |
Coast |
Coastal zone dominated by South Lantau Road, lagoon,
beaches and woodland with mature trees; coast accessible via paths through
woodland or small roads. Cheung Chau Typhoon Shelter along Sai Tai Road
typical fishing village settings. |
High |
LCU6 |
Rock Shore |
Natural Rocky Shore-line along Tai Long Wan in Chi Ma Wan
Peninsula, adjacent to mature woodland on hillsides, inaccessible by
footpaths or roads. |
High |
LCU7 |
Harbour/ Boatyards |
Boatyards facilitate Cheung Chau kai-to and fishery
located at north and south ends of Sai Tai Road. |
Low |
LCU8 |
Promenade |
Promenade with artificial sea wall, ferry pier and kai-to
pier, located at Cheung Chau Sai Tai Road. Tree Planting found along the
promenade adjacent to village houses with GF commercial activities. |
Medium |
In accordance with the study methodology, the
Sensitive Visual Receivers (SVRs) within the visual envelope were identified,
and grouped into types. (refer
to Table 8-4 )and Selected photographic
records of the significant key views from SVRs are shown on Figure 8.7 .10-8.12).
In summary, the SVRs can be classified into six main groupings according to the
location of the proposed works as defined in Table 8-3.
Table
8-3 Classification of Sensitive
Visual Receivers (VSRs)
Section |
Description |
SVRs |
1 |
Pui O Substation to Pui O Beach |
SVR 1.1, 1.2,
2.1, 2.2, 4 & 5 |
2 |
Pui O Beach to
Tai Long Wan east using cable tunnel |
Section Not Visible |
2a |
Pui O tunnel portal |
SVR 3 & 4 |
3 |
Tai Long Wan
to Cheung Chau Sai Tai Road using submarine cable |
Section Not Visible |
3a |
Tai Long Wan landfall area |
SVR 6, 7 & 8 |
3b |
Cheung Chau
Sai Tai landfall area |
SVR 9.1 & 14 |
4 |
Cheung Chau
Sai Tai Road to Cheung Chau South Station using underground cable |
SVR 9.3, 10, 13 & 14 |
5 |
Cheung Chau
Sai Tai Road to Cheung Chau North Station using underground cable |
SVR 9.1, 9.2,
9.3, 10, 11, 12, 13, 14, 15 |
Detail project description refer to Table 8-.1
Table 8-4 Summary of
Sensitive Visual Receivers (SVRs)
SVR |
Name |
Nature
of Viewer Group |
Distance
to Proposed Works |
Frequency
and duration of view towards proposed development and source of impact Type
of view |
Sensitivity
to change and visual intrusion |
SVR1.1 |
Pui O South Village Development (approximate number of receivers: small) |
Residents at Ham Tin Tsuen |
Approx. 200m to nearest point |
Elevated and partial views of Section 1
toward Chi Ma Wan Road |
Medium |
SVR1.2 |
Pui O North Village Development (approximate number of receivers: moderate) |
Residents
at Lo Wai Ts |
varies between 20m
to 200m |
Elevated and partial views of Section 1
toward Lantau South Road |
Medium |
SVR2.1 |
Chi Ma Wan Road (approximate number of receivers: small) |
Users + Pedestrians |
Crosses alignment of project |
Unobstructed overview of Section 1 in
foreground |
Medium |
SVR2.2 |
Lantau South Road (approximate number of receivers: moderate) |
Users
+ Pedestrians |
Crosses alignment of project |
Unobstructed overview of Section 1 in
foreground |
Medium |
SVR3 |
Pui O Wan Beach camp site (approximate number of receivers: moderate) Noted: Hostel on Pui O Beach is abandoned for
years which is not considered as SVR. |
Visitors |
Approx.300m to 1000m to nearest point |
Low unobstructed overview of Section 2a
across the river |
Medium |
SVR4 |
Village houses near Tin Hau Temple (Pui
O Wan) (approximate
number of receivers: small) |
Residents
at couples of village houses |
Approx. 100m to 150m to nearest point |
Low unobstructed overview of tunnel portal |
High |
SVR5 |
Detached Houses (Pui O Wan) (approximate number of receivers: small) |
Residents
in 10 detached houses |
Varies between 100m
and 200m |
Low partial views of Section 1,
screening by foreground vegetation |
High |
SVR6 |
On Kai-to along Adamasta Channel (approximate number of receivers: small) |
Passengers |
Varies between 100m
and 2000m |
Oblique and unobstructed views of
Section 3b, & 5 and partial
views of Section 3a |
Low |
SVR7 |
Tai Long Wan (approximate number of receivers: small) |
Visitors
to the beach & walking trail. |
Varies between 100m
and 2000 m |
Elevated and partial views of Section 3a |
Low |
SVR8 |
Sea Ranch Yi Long Wan (approximate number of receivers: small) |
Visitors
to the resort & the waking trail + Residents in the resort |
Approx. 2500m to the
nearest point |
Partial views of Section 3a |
Low |
SVR9.1 |
Cheung Chau Central Village Development
(approximate number of receivers: moderate) |
Residents + Students + Staffs
along Pak She P |
Varies between 10m to 800m |
Unobstructed overview of Sections 5 in
foreground at Ground level along Pak She Pra |
High |
SVR9.2 |
Cheung Chau North Village Development (approximate number of receivers: moderate) |
Residents
at Cheung Kwai Estate, Pak She San Tsuen. |
Varies between 100m to 300m |
Elevated and partial views of Section 5
towards the Cheung Chau North Station, North
Pek She Parya Road and Parya Street |
High |
SVR9.3 |
Cheung Chau South Village Development (approximate number of receivers: moderate) |
Residents
at the south end of Sai Tai Road, include Greenery Crest and Round Table 1st
Village |
Varies between 100m to 300m |
Elevated and unobstructed overview of
Sections 3b in foreground near the south end of Sai Tai Road; partial views
of Section 4 & 5 between buildings. |
High |
SVR10 |
Rest Garden at Cheung Chun Road (approximate number of receivers: small) |
Users & Visitors |
Crosses alignment of
project |
Unobstructed overview of Section 4 & 5 in foreground |
High |
SVR11 |
Cheung Chau Central Kai-to Pier (approximate number of receivers: moderate) |
Visitors + Passengers |
Crosses alignment of
project |
Partial views of Section 5 in foreground |
Medium |
SVR12 |
Tung Wan Road (approximate number of receivers: moderate) |
Users |
Approx. 50m to the
nearest point. |
Low and partial views of Section 5 |
Medium |
SVR13 |
Cheung Chau Promenade (approximate number of receivers: moderate) |
Users + Visitors |
Crosses alignment of
project |
Unobstructed overview of Sections 4 &5 in foreground |
Medium |
SVR14 |
Cheung Chau Typhoon Shelter (approximate number
of receivers: moderate) |
Visitors + Residents
on boat |
Varies between 100m
to 1000m |
Partial views of Sections 3b, 4 & 5
from the sea |
Medium |
SVR15 |
Pak She Forth Lane Seafood Restaurant (approximate number of receivers: moderate) |
Visitors +Residents
at the 2nd & 3rd
levels above the restaurants |
Cross alignment of
project |
Unobstructed overview of Section 5 in foreground |
High |
The starting point for the review of the planning
and development control framework was a reviewa review of the
various statutory and non-statutory controls relevant to the proposed project,
which affect landscape and visual impacts.
The review includes information on:
·
South West New Territories Development Strategy Review
·
The Draft South Lantau Coast Outline Zoning Plan (OZP)
No. S/SLC/11
·
The Cheung Chau South Layout Plan L/I-CCS/2C
·
The Cheung Chau Central Layout Plan L/I-CCC/2
·
The Cheung Chau North L/I-CCN/IB
South West New Territories Development Strategy Review (SWNT TDSR) (July 2001)
The main objective of the Recommended Development Strategy for SWNT is to provide a sustainable development framework to guide the detailed planning and development for SWNT up to the year 2016 and possibly beyond. This planning framework has included broad land use concepts for the sub-region, highlighting the strategic roles and functions of respective areas and indicating the scope of development that could take place. It highlights the role SWNT in fulfilling the long-term territorial needs and balance development and conservation needs within the area. In terms of conservation and landscape, TDRS Board Conservation Strategy is formulated for the unique and significant land and marine resources within SWNT;. The following summaries the relevant key landscape and visual issues in TDSR:
Planning issues in Conservation and Landscape
· Central Lantau, South Lamma, Sunshine Island, Po Toi Islands and Soko Islands are highlighted as Significant Land Conservation Areas. The water bodies in Southwest Lantau and South Lamma are designated as Unique Marine Conservation Areas while Cheung Chau, Po Toi Islands, South East Lantau and Soko Islands as Significant Marine Conservation Areas. These conservation areas form the basis for the formulation of the development strategy for SWNT;
· There are ten designated Sites of Special Scientific Interest (SSSI) and a number of designated sites of conservation importance;
· The potential for further development in SWNT should be carefully examined and supported by detailed assessments, without compromising the unique conservation areas and high quality landscape features. For such developments, all adverse impacts on the environment must be minimized and mitigated to an acceptable level. Tourist/ Recreational proposals also be sensibly integrated with the environment.
·
The proposed project will not conflict with any designated Site of Special Scientific
Interest (SSSI).
Recommended Development
Strategy
South Lantau Coast
· Conservation and Sustainable Recreation is recommended as the key planning theme for South Lantau. Sustainable recreation development is recommended.
· To provide proper management of the scenic resources and protection of the natural attributes within SWNT, about 7,840 ha of Lantau Island are designated as Country Parks under the Country Parks Ordinance.
· About 4,780 ha of rural areas which fall outside the identified urban development areas, Country Parks and potential Country Parks are mainly designated as 'Conservation Area'. These areas are classified either as 'Landscape Protection Area' or 'Coastal Protection Area' depending on the nature of attributes to be protected. The general planning intention is to protect the landscape and ecological values of these areas and/or to serve as a buffer against encroachment of urban development into the Country Parks, the Special Areas and SSSIs. Whilst there is a general presumption against developments in these areas, redevelopment and expansion of recognized villages as well as some compatible low-intensity recreational uses may be considered.
· The coastal areas are intended to be conserved mainly for water-based recreation and low-intensity recreational uses.
Cheung Chau
· Conservation, Recreation and Area-by-Area Approach Development is recommended as the key planning theme for Cheung Chau. An area-by-area approach is adopted to guide the land use schemes for the outlying islands so as to respect the distinct potential, character and resources of the respective islands.
· In view of the low-lying setting and the rural character, it is inappropriate to pursue major urban developments there.
· Some continued development is envisaged in Cheung Chau.
The Draft South Lantau Coast Outline Zoning
Plan (OZP) No. S/SLC/11
The main landscape features defined by the current Draft South Lantau Coast OZP No. S/SLC/11, are limited to the Country Park (CP), Coastal Protection Area (CPA), Green Belt (GB) and Village Type Development (V). The OZP illustrates and provides broad principles concerning development within the defined planning area. This review has made reference to the plan and the Notes and the Explanatory statement. Key issues are briefly listed below:
Country
Park (CP) - to encourage
recreation and tourism, protect vegetation and wildlife, preserve and maintain
buildings and sites of historical or cultural significance within country parks
and to provide facilities and services for the public enjoyment of the country.
(Note: the term 'Country Parks' includes 'Special
Areas' designated under the Country Parks Ordinance)
Coastal Protection Area (CPA) - to retain natural coastline.
The South Lantau Coast OZP indicates that land immediately to Pui O Beach
is zoned Coastal Protection Area (CPA) or Green Belt (GB). The planning intention of a CPA is to
protect the natural character of the shoreline, to safeguard the beaches and
adjacent hinterland, and to prevent haphazard development along South Lantau
Coast. The planning function of a GB
is:
Green Belt (GB) - define the limits of urban development areas by conserving landscape features.
Planning intention is to reserve the existing topography and natural vegetation and to provide a buffer between existing village and the countryside to the south. To the southeast, most of Chi Ma Wan Peninsula is zoned Country Park (CP).
The Cheung Chau South Layout Plans shows land along Sai Tai Road is zoned
Promenade and adjacent to the existing villages which is zoned Village Type
Development (V) which is:
Village Type Development Zone (V) - controlled under New Territories Exempted Houses conditions i.e. not exceed 65m2, 8.23 max. height and 3 storeys.
The presence of CP, GB and CPA zonings within the study area suggests that the quality of parts of the landscape is high and it is also regionally important.
Cheung Chau South Layout Plan L/I-CCS/2C, Cheung Chau Central Layout
Plan L/I-CCC/2 & Cheung Chau North L/I-CCN/IB
Although the captioned plans are non-statutory, it is a supporting planning document which government outlines provide the future pattern of development. Main landscape features are briefly listed below:
Building height
Village Type Development zone‘V’ is controlled under N.T.E.H. conditions i.e. not exceed 65m2, 8.23 max. height and 3 storeys.
Pedestrian and Emergency access way
Zoned along the Pak She Paya Road along Pak She Parya Road, Parya Street and Tai Hing Road and Sai Tai Road. Existing trees are located.
Countryside Conservation Area (CCA)
East of Cheung Chau South and northeast of Cheung Chau North are zoned as CCA to conserve the natural setting of the countryside.
Coastal Protection Area (CPA)
Southeast Cheung Chau Central is zoned as CPA to protect the natural coastal characters.
Amenity Area (A), District Open Space (DO) and Local Open (LO) are located within the village settlement of Cheung Chau
The
alignment of the proposed project traverses sections of Lantau South Country
Park, zoned as Country Park (CP) and
through an area zoned Coastal Protection
Area (CPA) which the Town Planning Ordinance permits statutory land use
zones under clause 4(1)(g) for 'country parks, coastal protection areas, sites
of special scientific interest, green belts or other specified uses that
promote conservation or protection of the environment'. land-useLand-use zonings
controlling development within the study area (refer to Figure. 8.813 )) The alignment in
Cheung Chau (Section 3b, 4 & 5) traverses the Pedestrian and Emergency
access way and surrounded by areas zoned as Village Type Development, Amenity
area, Local Open Space and Government institution. Conflicts related landscape and visual impacts to the existing
planning and development control framework are shown in Table 8-5listed
below:.
Table 8-5 Conflicts Related
Landscape and Visual
Impacts to the Existing
Planning and Development
Control Framework
Section |
Conflicts |
Follow-up
action |
Section
1, 4 & 5 |
constructed along the Lantau South Road and Chi Ma Wan Road, no conflicts to the existing
controls. |
not necessary |
Section
2 |
Underground Tunnel , no
conflicts to the existing controls. |
not necessary |
Section
3 |
Submarine Cable, no conflicts to
the existing controls. |
not necessary |
Section
2a,3a &3b |
Pui O Tunnel portal and Tai Long Wan Landfall areas conflict with the Country Park (CP) zone and the
development strategy for South Lantau Coast in the SWNT TDSR Cheung Chau Sai Tai landfall areas constructed along the Pedestrian and
Emergency access way, no conflict
with the existing controls. |
No planning application is required
(PlanD ref:() in SKI/L/GEN/22) Permission for erect or construct any building in country park is
required from AFCD |
Detail project description
refer to Table 8-.1
A landscape impact is a physical change to an
existing landscape resources. By mapping
the extent and location of these changes, any loss or alteration can be
assessed and, where possible, re-provisioned or compensated by landscape
mitigation measures incorporated into a Project.
The
significant landscape impacts of the proposed project are predicted from
construction and demolition activity during the construction phase except
Section 2 & 3. Minor landscape impacts are predicted during the
operation phase except for Pui O tunnel portal (Section 2a) and landfall areas
(Sections 3a and 3b). The
predicted landscape impacts are as follows (refer to Figure 8.14):
Construction
Phase
Disturbance to topsoil and
vegetation - The construction and demolition activity such as excavation,
storage of construction materials and the movement of machinery will result in
the disturbance to topsoil and vegetation and this impact could be high in
parts owing to the regional value of the landscape. Refer to Table 8-.1 . Delivery of
construction material to tunnel portals and landfall areas (Sections 1, 2a, 3a and, 3b) is to be by
barge via temporary landing area access area at Tai Long Wan and by road at
Pui O. For the remote areas within Chi
Ma Wan Peninsula construction materials will be delivered by helicopter,
thereby avoiding the need to construction extensive access tracks and the
subsequent destruction of natural vegetation.
Generally construction material will be delivered as close as possible
to designated location minimising affect on existing trees, but will result in
disturbance to the natural ground. The disturbed area and the tree survey
report are summarummariseieds
in Tables 8-6
and 8-7
respectivelybelow:.
Table 8-6 Description
of Disturbed Area
Section |
Description |
Disturbed Vegetated Area |
Works Area |
1 |
Pui O Substation
to Pui O Beach |
Nil |
Nil |
2 |
Pui O Beach to Tai Long Wan east using
cable tunnel |
Nil |
Nil |
2a |
Pui O tunnel
portal |
750m2 |
Cut slope: 750m2 |
3 |
Tai Long Wan to Cheung Chau Sai Tai
Road using submarine cable |
Nil |
Nil |
3a |
Tai Long Wan
landfall area |
1050m2 |
Cut slope: 700m2 Temporary access: 350m2 |
3b |
Cheung Chau Sai Tai landfall area |
Nil |
Nil |
4 |
Cheung Chau Sai Tai Road to Cheung Chau
South Station using underground cable |
Nil |
Nil |
5 |
Cheung Chau Sai Tai Road to Cheung Chau
North Station using underground cable |
Nil |
Nil |
|
Total |
1800m2 |
- |
Detail project description refer to Table 8-.1
Table
8-7
Summary of Tree Survey at Pui O Tunnel Portal (2a)
& Tai Long Wan Landfall Area (3a)
Description &
Possible Treatment |
Quantity |
Remark |
Total number of tree
surveyed |
87 Nr. |
- |
Tree proposed to be
felled |
38 |
Conflict with construction work (Common Species) |
Tree proposed to be
retained |
49 |
- |
Tree proposed to be
transplanted |
0 Nr. |
- |
Protected
species |
Aphyllorchis montana
(Orchid) |
2 colony (approx.200 number) |
Refer to the tTree sSurvey Report given in ( Appendix I), mostly common
species within this working area of Pui O tunnel portal (Section 2a) and Tai Long
Landfall area (Section 3a) are identified. Table
8-7 indicates that among 387 Common species
including Casuarina
equisetifolia, Schefflera
octophylla, Bredelia tomentosa, Aquilaria sinensis, Sapium discolor, Aporusa dioica,
Scolopia chinensis, Sterculia lanceolata, Fraxinus formosana, Acronychia pedunculata, Microcos
paniculata and Ficus microcarpa are proposed to be felled. A
protected orchid species, Aphyllorchis
montana was found in the proposed Pui O Tunnel Portal
(Section2a). It comprises two colonies.
For detail assessment refer to the Tree Survey Report for
Pui O Tunnel Portal and Tai Long Wan Landfall Area. The
corresponding landscape mitigation measures are discussed in section sub-clause 8.8 - Recommended Mitigation Measures. In
summary, the construction of the proposed works will affect 1800m20.15 ha.
of existing vegetation.
Disturbance to coastal area line which is and rocky/sandy
shore -– The reclamation activity, cutting
slopes and temporary structures for construction and materials delivery in
Sections 2a, 3a and 3b, including access road will result in significant
impacts on Landscape Character Units LCU4.1, LCU5 and LCU6. Table 8-8 summarises the findings of the
disturbed coastal areas.
Table 8-8 Description of Disturbed
Coastal Area
Section |
Description |
Disturbed Coastal Area |
Length of Disturbed Coastline |
Works Area |
1 |
Pui O Substation
to Pui O Beach |
Nil |
Nil |
Nil |
2 |
Pui O Beach to Tai Long Wan east using
cable tunnel |
Nil |
Nil |
Nil |
2a |
Pui O tunnel
portal |
180m2 |
80m |
|
3 |
Tai Long Wan to Cheung Chau Sai Tai
Road using submarine cable |
Nil |
Nil |
Nil |
3a |
Tai Long Wan
landfall area |
Nil |
Nil |
Nil |
3b |
Cheung Chau Sai Tai landfall area |
100m2 |
6m |
Temporary disturbance on the artificial seawall |
4 |
Cheung Chau Sai Tai Road to Cheung Chau
South Station using underground cable |
Nil |
Nil |
Nil |
5 |
Cheung Chau Sai Tai Road to Cheung Chau
North Station using underground cable |
Nil |
Nil |
Nil |
|
Total |
280m2 |
- |
- |
Detail project description
refer to Table 8-.1
· The majority of the underground cables (Sections 1 ,4 and 5) will be laid under existing roads and therefore the landscape impact would be low during construction (and negligible during operation)
·
The underground cable in tunnel (Section 2) will be
buried underground all the way except at the tunnel portal locations (Section
2a), therefore visual and landscape impacts are negligible. The temporary
reclaimed works areatemporary working platform (180m2)
will probably be reinstated and landscaped
with minor change in the local landscape context.
·
The submarine cable will be landed at the Round Table
of Cheung Chau Sai Tai Road, moderate to significant adverse impacts due to
temporary disturbance of manmade artificial promenade during construction.
Total area of the disturbed promenade is 100m2.
0.012ha. The
existing promenade will be reinstated during operation, slight adverse
landscape impact will be observed.
Operation Phase
·
The cables will be laid underground and therefore the
long term landscape impact is predicted to be low except for specific locations
(Refer to Table 8-.1see below)
·
Tunnel portal, temporary reclaimed
works areatemporary working platform (Pui O only) and
Tai Long Wan landfall areas are to be constructed at Pui O and Tai Long Wan
East. Disturbance to existing woodland, coastal area line and rocky
shoreline will be moderate to moderate-significant adverse at Day 1, but
with reinstatement the proposals (including re-vegetating disturbed slopes and
re-instatement of shoreline) the impact at year 10 will be slight adverse.
Table 8-95
below summarises significance threshold of the landscape impacts during
construction and operation.
Table 8-95 Summary of Landscape Impacts (without
Landscape Mitigation Measures)
LCU Name |
Disturbed Area (Refer
to Section 8.7.1) |
Quality/ Sensitivity to Chang |
Construction
Phase |
Operation
Phase |
||
Magnitude of
Change and Source of Landscape Impact |
Significance
Threshold of Landscape Impact |
Magnitude of
Change during Operation Phase |
Significance
Threshold of Landscape Impact |
|||
LCU 1 Mixed Village & Agricultural Uses
|
Nil |
Low |
Low Delivery construction materials +
temporary hoarding |
Slight Adverse |
Negligible |
Negligible |
LCU 2 Township
|
Nil |
Low |
Moderate Delivery construction materials +
temporary hoarding |
Moderate Adverse |
Negligible |
Negligible |
LCU 3 Community Facility
|
Nil |
Medium |
Low Delivery construction materials +
temporary hoarding |
Moderate Adverse |
Negligible |
Negligible |
LCU 4.1 Woodland
|
1800m2 |
High |
High Delivery construction materials by +
temporary hoarding + associated structures of tunnel portal and landfall areas |
Significant Adverse |
Moderate |
Moderate Adverse |
LCU 4.2 Recreation
|
Nil |
High |
Low Delivery construction materials +
temporary hoarding |
Moderate Adverse |
Negligible |
Negligible |
LCU 5 Coast
|
180m2 |
High |
High Delivery construction materials by
boats or helicopters + temporary hoarding + associated structure of tunnel portal and landfall areas + small
scale |
Significant Adverse |
Moderate |
Moderate Adverse |
LCU 6 Rock Shore
|
Nil |
High |
High Delivery construction materials by boats or helicopters +
associated structures of tunnel
portal and landfall areas + small
scale |
Significant Adverse |
Negligible |
Negligible |
LCU
7 Harbour/ Boatyards
|
Nil |
Low |
Negligible Delivery construction materials + temporary hoarding |
Negligible |
Negligible |
Negligible |
LCU 8 Promenade
|
100m2 |
Medium |
High Delivery construction materials + temporary hoarding +
associated structures of tunnel
portal and landfall areas |
Moderate-Significant Adverse |
Low |
Slight Adverse |
A visual impact is a change to the appearance of
the study area, within the visual envelope, that affects individuals or groups
of people. Visual impact can vary in
significance from overall improvement to degradation. Its assessment relies on a professional understanding of
aesthetic principles, the design and function of cityscapes and landscapes, and
the characteristics of human perception.
Permanent and adverse levels of visual impact can lead to the blighting
of urban and rural areas, resulting in a long-term decline in the quality of an
environment.
The visual
impact study was conducted in accordance with Section 8.3. In summary, the visual impacts of the
proposed work will affect viewer groups at SVR locations mainly during
construction for except that affect by the permanent intrusion of the tunnel
portal and landfall (Sections 2a and 3a) (refer to Figure 8.14).
Table 8-106 below
summarises significance threshold of the visual impacts during construction and
operation.
Construction Phase
The visual impacts arising from disturbance of the existing visual context during construction will be:
· The intrusion of views southwards from properties near to the Pui O tunnel portal area will result in moderate-significant adverse visual impacts for SVRs 4 and 5.
· The intrusion of views southwards toward Tai Long Wan Tunnel Portal will result in slight to moderate adverse visual impacts for SVRs 6,7 and 8.
· The disruption and intrusion of views at the landfall area and promenade to sub-station at Cheng Chau will result in moderate-significant adverse visual impacts for SVRs 9,10,13 and 15.
· The disruption of views from SVRs near to the proposed works will result in slight-moderate adverse visual impacts for SVRs 11,12 and 14.
· The disruption of views towards the Lantau South Road and Chi Ma Wan Road from low level SVRs will result in moderate-significant adverse visual impacts during construction only for SVRs 1.2, 2.1 and 2.2
· The disruption of views towards the sea from low level SVRs along Cheung Chau village settlements will result in significant adverse to moderate adverse visual impacts for SVRs 9.1, 9.2 and 9.3 owing to their distances from the proposed work.
Operation Phase
The visual impacts arising from disturbance of the existing visual context during operation will be:
· Generally negligible impacts are predicted for the majority of SVRs as the completed works will be underground resulting in no discernible changes in existing visual quality.
· The tunnel portal areas will result in a noticeable change in the visual quality for SVRs 3 and 4; and
· SVRs 6 and 7 will experience a slight/barely noticeable change in visual quality.
Table 8-106 Assessment of Visual Impacts (without
Landscape Mitigation Measures)
SVR |
Name |
Sensitivity to Change and Visual
Intrusion (Refer to Table 8- |
Construction Phase |
Operation Phase |
||
Magnitude of Visual Change |
Significance Threshold of Visual
Impact |
Magnitude of Visual Change |
Significance Threshold of Visual Impact |
|||
SVR1.1 |
Pui
O South Village Development |
Medium |
Low |
Slight-Moderate Adverse |
Negligible |
Negligible |
SVR1.2 |
Pui
O North Village Development |
Medium |
High |
Moderate- Significant Adverse |
Negligible |
Negligible |
SVR2.1 |
Chi Ma Wan Road |
Medium |
High |
Moderate-Significant Adverse |
Negligible |
Negligible |
SVR2.2 |
Lantau South Road |
Medium |
High |
Moderate-Significant Adverse |
Negligible |
Negligible |
SVR3 |
Pui O Wan Beach camp site |
Medium |
High |
Moderate-Significant Adverse |
Moderate |
Moderate Adverse |
SVR4 |
Village houses near Tin Hau Temple (Pui O Wan) |
High |
High |
Significant Adverse |
Moderate |
Moderate-Significant Adverse |
SVR5 |
Detached Houses (Pui O Wan) |
High |
Low |
Moderate Adverse |
Low |
Negligible |
SVR6 |
On kai-to along Adamasta Channel |
Low |
Low |
Slight Adverse |
Low |
Slight Adverse |
SVR7 |
Tai Long Wan |
Low |
Low |
Slight Adverse |
Low |
Slight Adverse |
SVR8 |
Sea Ranch Yai Long Wan |
Low |
Low |
Slight Adverse |
Low |
Negligible |
SVR9.1 |
Cheung Chau Central Village Development |
High |
High |
Significant Adverse |
Negligible |
Negligible |
SVR9.2 |
Cheung Chau North Village Development |
High |
Low |
Moderate Adverse |
Negligible |
Negligible |
SVR9.3 |
Cheung Chau South Village Development |
High |
Moderate |
Moderate-Significant Adverse |
Negligible |
Negligible |
SVR10 |
Rest Garden at Cheung Chun Road |
High |
Moderate |
Moderate-Significant Adverse |
Negligible |
Negligible |
SVR11 |
Cheung Chau Central Kai-to Pier |
Medium |
Low |
Slight-Moderate Adverse |
Negligible |
Negligible |
SVR12 |
Tung Wan Road |
Medium |
Low |
Slight-Moderate Adverse |
Negligible |
Negligible |
SVR13 |
Cheung Chau Promenade |
Medium |
High |
Moderate-Significant Adverse |
Negligible |
Negligible |
SVR14 |
Cheung Chau Typhoon Shelter |
Medium |
Low |
Slight-Moderate Adverse |
Negligible |
Negligible |
SVR15 |
Pak She Forth Lane Seafood Restaurant |
High |
High |
Significant Adverse |
Nil |
Negligible |
The assessment studies in the previous section
predict that the majority of landscape and visual impacts during construction
will be moderate to significant adverse and
negligible impacts during
operation. However, there are a number
of exceptions, namely a “moderate to significant adverse” landscape impact to
the Woodland LCU 4.1 and Coastal Area LCU5 during construction and “moderate-/significant adverse” visual
impacts to viewer groups at SVRs 3 and 4 during construction and
operation. The sources landscape impact
arises from construction activities, such as slope cutting for the tunnel
portal, formation of a temporary working platformreclamation
works and access in Sections 2 and 4. The source of the visual impact is the permanent intrusion of
tunnel portal and landfall areas in proximity to residents and recreation area
during the construction and operation phase for viewer groups at SVRs 3, 4, 6
and 7.
In order to mitigate these impacts, a number of
on-site landscape mitigation measures are recommended for incorporation into
the Project. The mitigation measures
are summarised in the following paragraphs. No off-site mitigation measures
have been proposed. (refer to Tables
8-11.7
& 8-12.8 and Figure 8.915).
The construction programme for the Project should be reduced
to the shortest possible period and should be executed in phases, particularly
in those locations where severe or high landscape and visual impacts are
expected such as Pui O tunnel portal.
Additionally, the extent and periphery of the works areas should be
managed so that they are as small as possible and do not appear cluttered,
untidy and unattractive, particularly to pedestrians and people undertaking
recreation activities in the Country Parks, beach and Cheung Chau Promenade. Measures should be implemented during
construction to prevent soil erosion, such as temporary drainage around
excavations, covering of topsoil stockpiles with impermeable material and
sandbagging diversions around exposed soil. Temporary hoarding
barriers should be of a recessive visual appearance in both colour and form.
Measures should be implemented during construction to store materials in areas
with the least obstruction to residents, pedestrians and traffic and cover all
material stockpiles with impermeable material and sandbagging diversions around
exposed soil. The temporary reclaimed working platformarea
at the Pui O portal is required for stockpiles from construction of the tunnel
portal. Topsoil will also be stockpiled
and used in the restatementreinstatement of
the disturbed coastline after construction. And those stockpiles should not be
more than 2m high.
Where possible, the transplantation of existing valuable
trees affected by the proposed works and new compensatory planting works;
should be carried out as early as possible in the construction period instead
of at the end. This will allow the
maximum time for maintenance, resulting in a higher success rate for the
survival of transplanted trees and the early establishment of new screen trees
and compensatory planting.
The protected orchid species, Aphyllorchis montana which was found in
the area of the Pui O Tunnel
Portal (Section2a) should be temporarily moved to a new location on site and
carefully monitored and maintained.
Following completion of the construction works they should be reinstated
in a condition and suitable location as near as possible to the original
habitat.proposed Pui O Tunnel Portal (Section 2a) is proposed
to be transplanted.
In compensation for the disturbance, a planting
reinstatement scheme will be implemented as shown on Figure 8.915. It will comprise replanting 750 m2 of
the Pui O tunnel portal area and 700 m2 of the Tai Long Wan landfall
area with similar tree species to those found in the existing environs, on a
minimum 1 to 1 basis, a matrix of nursery stock seedlings and transplants are
proposed at a rate of 1/m2. A 2412-month
maintenance (i.e. defects liability) period will also be needed to ensure
transplantation in successful. (refer to Figure 8.915).
The design of the tunnel portal, and landfall areas should
incorporate materials, details and textures so as to be as visually recessive
as possible and in a style that fits with the surrounding rural setting. Colour
should be of low chromatic intensity to reduce the potential contrast between
the structures and their background. External finishing of the tunnel portal
and landfall area will be designed in conjunction with the landscape
scheme. Considering these two elements
in tandem will integrate and improve the visual mitigation of the overall
proposed works. Where possible the use of visually permeable security fencing
is recommended. This type of fencing will help to reduce the level of visual
impact of the portal building by maximising the ground width available for
planting. Grass-Crete planter incorporated onto the roof of the portal. (refer
to Figure 8.915).
The works areas at both Pui O and Tai Long Wan
Tunnel portals should be restored to their previous condition, including the
re-creation of natural and rocky shoreline, footpath and re-establishment of
disturbed vegetation. Topsoil dredged out during construction of the tunnel
will be used in restatementreinstatement of
the disturbed coastline. Where mature trees are felled that are considered high
in environmental amenity, a replacement semi-mature tree should be planted.
Existing trees cleared by construction activity should be replaced so that
there is a net gain in tree numbers after the project is completed. (refer to Figures 8.11 & 8.1216-8.19).
The significance of the landscape and visual
impacts assuming mitigation measures included in the Project was examined in
accordance with Section 8.3. Generally
mitigation measures will not reduce adverse impacts significantly during
construction, however they will reduce adverse impacts during the operation
phase. The findings of the LVIA are as follows.
A summary of residual landscape
impacts is shown in Table 8-117. In general, the incorporation of mitigation
measures into the Project will be effective in reducing “significant adverse”
construction impacts in the Woodland LCU 4.1 and Coastal Area LCU 5 to
“moderate-significant adverse”, and “moderate-/significant adverse” to “slight
adverse” during operation. These reductions can be achieved by the mitigation
measures recommended in Section 8.8. (refer to Figures
8. 11
& 8.1216-8.19).
A summary of residual visual impacts is shown
in Table 8-8. Where SVRs experience
“slight-/moderate
adverse” and “slight adverse” visual
impacts with the implementation of the recommended mitigation measures these
locations will experience “slight adverse” and visual impacts during operation.
(refer to Figures
8. 11 & 8.1216-8.19).
Using the criteria as set out in Section 8.3, the significance of these residual visual impacts are evaluated as being acceptable with mitigation measures owing to:
· the proposed engineering work incorporates landscape and visual mitigation measures, which will reduce overall adverse levels of visual impact to a slight –negligible level, and reduce the significant adverse impacts on the SVRs immediately adjacent the proposal to a slight adverse level of impact.
· the change to the baseline condition will be negligible except Sections 2, 4 and 5;
· in some locations, Cheung Chau Sai Tai Road (Section 5), the proposed alignment can be sited to avoid disturbance to existing trees and features along the promenade.
· All potentially high landscape impacts can be reduced or offset to a large extent by landscape mitigation measures.
The Landscape and Visual Impact
Assessment highlights that the significant adverse impacts will occur during
the construction phase. Significant impacts are also restricted to particular
locations, namely Pui O tunnel and Tai Long Wan tunnel portals and Cheng Cheung Chau landfall
area. The disturbed coastline at temporary working platformreclaimed woks areas
at Pui O tunnel portal and temporary access for delivery of materials at Tai
Long Wan Landfall area will be reinstated to the existing coastline after
construction. With mitigation measures, mentioned in Section 8.8, the long term
adverse impacts will be negligible. The alignment of the circuit is
significantly constrained by the technical engineering requirements. However, the nature of the proposed works
and construction methodology means that much of the cable can be constructed
with minimal disturbance to the existing landscape owing to the limited working
boundary along existing roads, footpaths.
Therefore, the proposed works will have limited adverse impacts or negligible
impacts on baseline condition with appropriate mitigation measures. In
conclusion, the landscape and visual impacts are considered acceptable with
mitigation measures.
Table 8-117 Summary of Residual Landscape Impacts
(with Landscape Mitigation Measures)
LCU Name |
Without Recommended
Mitigation Measures (Refer to Table 8-9 |
Recommended Mitigation Measures (Refer to Section 8- |
With Recommended Mitigation
Measures |
||
Significance Threshold of
Landscape Impact during Construction |
Significance Threshold of
Landscape Impact during Operation |
Significance Threshold of
Landscape Impact during Construction |
Significance Threshold of
Landscape Impact during Operation |
||
LCU 1 Mixed Village &
Agricultural Uses
|
Slight Adverse |
Negligible |
LMM1 |
Slight Neutral |
Negligible |
LCU 2 Township
|
Moderate Adverse |
Negligible |
LMM1 |
Slight Adverse |
Negligible |
LCU 3 Community Facility
|
Moderate Adverse |
Negligible |
LMM1 |
Slight Adverse |
Negligible |
LCU 4.1 Woodland
|
Significant Adverse |
Moderate-Significant Adverse |
LMM1, LMM2, LMM3, LMM4 |
Moderate-Significant Adverse
|
Slight Adverse |
LCU 4.2 Recreation
|
Moderate Adverse |
Negligible |
LMM1 |
Slight Adverse |
Negligible |
LCU 5 Coast
|
Significant Adverse |
Moderate-Significant Adverse |
LMM1, LMM2, LMM3, LMM4 |
Moderate-Significant Adverse |
Slight Adverse
|
LCU 6 Rock Shore
|
Significant Adverse |
Negligible |
LMM1, LMM2, LMM3, LMM4 |
Moderate-Significant Adverse |
Negligible |
LCU
7 Harbour/ Boatyards
|
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
LCU 8 Promenade
|
Moderate-Significant Adverse |
Slight Adverse |
LMM1 |
Moderate Adverse |
Negligible |
Table 8-128 Summary of Residual Visual Impacts (with
Landscape Mitigation Measures)
SVR Number |
Without Recommendation Mitigation Measures |
Recommended
Mitigation Measures |
With Recommendation Mitigation Measures |
|||
Significance Threshold of Visual Impact during
Construction |
Significance Threshold of Visual Impact during Operation |
Significance Threshold of Visual Impact during
Construction |
Significance Threshold of Visual Impact during Operation |
|||
DAY 1 |
YEAR 10 |
|||||
SVR1.1 |
Slight-Moderate Adverse |
Negligible |
LMM1 |
Slight Adverse |
Negligible |
Negligible |
SVR1.2 |
Moderate- |
Negligible |
LMM1 |
Moderate Adverse |
Negligible |
Negligible |
SVR2.1 |
Moderate-Significant Adverse |
Negligible |
LMM1 |
Moderate Adverse |
Negligible |
Negligible |
SVR2.2 |
Moderate-Significant Adverse |
Negligible |
LMM1 |
Moderate Adverse |
Negligible |
Negligible |
SVR3 |
Moderate-Significant Adverse |
Moderate Adverse |
LMM2, LMM3, LMM4 |
Moderate Adverse |
Slight Adverse |
Negligible |
SVR4 |
Significant Adverse |
Moderate-Significant Adverse |
LMM2, LMM3, LMM4 |
Moderate Adverse |
Slight Adverse |
Negligible |
SVR5 |
Moderate Adverse |
Negligible |
LMM1 |
Slight Adverse |
Negligible |
Negligible |
SVR6 |
Slight Adverse |
Slight Adverse |
LMM1, LMM2, LMM3, LMM4 |
Slight Adverse |
Negligible |
Negligible |
SVR7 |
Slight Adverse |
Slight Adverse |
LMM2, LMM3, LMM4 |
Slight Adverse |
Slight Adverse |
Negligible |
SVR8 |
Slight Adverse |
Negligible |
LMM2, LMM3, LMM4 |
Slight Adverse |
Negligible |
Negligible |
SVR9.1 |
Significant Adverse |
Negligible |
LMM1 |
Moderate Adverse |
Negligible |
Negligible |
SVR9.2 |
Moderate Adverse |
Negligible |
LMM1 |
Slight
Adverse |
Negligible |
Negligible |
SVR9.3 |
Moderate-Significant Adverse |
Negligible |
LMM1 |
Slight
Adverse |
Negligible |
Negligible |
SVR10 |
Moderate-Significant Adverse |
Negligible |
LMM1 |
Slight Adverse |
Negligible |
Negligible |
SVR11 |
Slight-Moderate Adverse |
Negligible |
LMM1 |
Negligible |
Negligible |
Negligible |
SVR12 |
Slight-Moderate Adverse |
Negligible |
LMM1 |
Negligible |
Negligible |
Negligible |
SVR13 |
Moderate-Significant Adverse |
Negligible |
LMM1 |
Slight Adverse |
Negligible |
Negligible |
SVR14 |
Slight-Moderate Adverse |
Negligible |
LMM1 |
Slight Adverse |
Negligible |
Negligible |
SVR15 |
Significant Adverse |
Negligible |
LMM1 |
Moderate Adverse |
Negligible |
Negligible |