This section presents the assessment of potential landscape
and visual impacts associated with the construction and operation of the Pilot
Project for Public-Private Partnership Conservation Scheme, Sha Lo Tung Valley,
Tai Po.
The methodology of the LVIA is 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 and the EIAO Guidance Note No. 8/2010 “Preparation
of Landscape and Visual Impact Assessment Under the
Environmental Impact Assessment Ordinance.”
The landscape assessment for both the Development
Site and Sha Lo Tung Road Upgrade consider the source and magnitude of
development effects on the existing landscape elements, character and quality
in the context of the site and its environs.
The landscape impact assessment will cover the following:
·
Describe
the baseline landscape within 500m of the Project and the works area of the
enabling works along the access routes.
·
Describe
the Landscape Character Areas (LCAs) and Landscape
Resources (LRs) including describing edges as
different LRs.
·
Map
the distribution of the LCAs and LRs.
·
Propose
a qualitative and quantitative assessment of significant thresholds which
reflect the magnitude of change and sensitivity of a particular LCAs and LRs.
·
Analyse
the landscape impacts during construction, impact after development, and
off-site landscape impacts. This section
analyses the extent to which these landscape units and edges are changed, using
both quantitative and qualitative assessments.
·
Examine
landscape design measures that will avoid creating Landscape Impact, these may
include adjustments to building sitings, road
alignments etc that reduce landscape and visual impacts.
·
Examine
landscape measures that will contribute to reducing any landscape impacts or
will enhance the landscape associated with the Proposed Development &Road
Upgrade. They may include planting, new landscaped areas and
re-vegetation. The residual landscape
impacts are also analysed.
·
Provide
conclusions on the Landscape impacts of the Project.
The visual impact assessment provides an identification
of the visual envelope and analyses the source and magnitude of effects caused
by the proposed development on the existing views, visual amenity, character
and quality of the Visually Sensitive Receivers (VSR) within the context of the
site and its environs. The key steps involved include:
·
Define
the visual envelope that would be potentially impacted by the Project to
determine areas that could potentially see the development. This GIS visual envelope analysis was based
solely on topography and did not take into account the screening potential of
vegetation, which would further reduce the actual visual envelope. The GIS visual envelope analysis also mapped
the visibility of the development from roads and houses.
·
Select
indicative viewpoints to
prepare photomontages to assist in assessing the visual impact on the broader
landscape. In order to illustrate the landscape and visual impacts of the
proposed Columbarium and the Sha Lo Tung Road improvement works, photomontages
at selected viewpoints have been prepared to provide a preliminary illustration
of both the existing conditions, the unmitigated conditions after construction
and the mitigated conditions at day 1 and year 10. The residual impacts have been evaluated
qualitatively.
·
Predict
the impact significance on the Visually Sensitive Receivers (VSR) within the
visual envelope.
10.3
Relevant
Legislation and Guidelines
Relevant legislation, standards and guidelines
include:
·
Forests and Countryside Ordinance (Cap. 96) and its subsidiary legislation
the Forestry Regulations;
·
Town Planning Ordinance (Cap 131);
·
Protection of Endangered Species of Animal
and Plants Ordinance (Cap 586);
·
Country Parks Ordinance (Cap 208);
·
Environmental Impact Assessment Ordinance (Cap.499, S.16) and the Technical
Memorandum on EIA Process (EIAO TM), particularly Annexes 10, 11, 18, 20 and 21;
·
EIAO Guidance Note 8/2010;
·
Sha Lo Tung Outline Zoning Plan No.S/NE-SLT/4;
·
Hong
Kong Planning Standards and Guidelines;
·
Work Branch Technical Circular (WBTC) No. 25/93 - Control of Visual Impact of
Slopes;
·
SILTech
Publication (1991) – Tree
Planting and Maintenance in Hong Kong (Standing Interdepartmental Landscape
Technical Group) [11-23];
·
WBTC No. 17/2000 – Improvement to the Appearance of slopes
in connection with WBTC 25/93;
·
WBTC No. 7/2002 – Tree Planting in Public Works;
·
ETWB TC (Works) No. 2/2004 : Maintenance of Vegetation and Hard
Landscape Features;
·
ETWB TC (Works) No. 29/2004 : Registration of Old and
Valuable Trees, and Guidelines for their Preservation;
·
ETWB TC (Works) No. 11/2004 – Cyber Manual for Greening;
and
·
ETWB TC (Works) No. 3/2006 - Tree Preservation.
10.4
The Development
Site - Existing Site Location
The site for the proposed Project area is at Sha Lo
Tung in the New Territories, in Hong Kong SAR.
The Development Site is located approximately 1 km north of the
outskirts of the city of Tai Po. The
Site is located in an undulating area with hill slopes to the east, north and
west.
A detailed project description is provided in Section 3 of this EIA and the Concept
Design Plan is presented in Annex B.
No demolition works are required as part of this
development.
The site formation works of the Development Site will
take approximately 14 months and total construction is expected to take 18
months. A detailed construction program
is provided in Section 3.
The project areas are located within the Sha Lo Tung Outline
Zoning Plan S/NE – SLT/4 and the Tai Po Outline Zoning Plan No. S/TP/23 (Refer Section 2). The Development Site and a part of the road
improvement works are located within the Sha Lo Tung OZP within an area defined
as ‘Greenbelt’.
The Planning Intention of this zone is primarily for
defining the limits of development areas by natural features, and to contain
urban sprawl as well as to provide passive recreational outlets. It is also
intended to serve as a buffer for the ‘Conservation Area’ and ‘Site of Special
Scientific Interest’ zones so as to conserve the existing rural character and
natural landscape. There is general presumption against development within this
zone.
The proposed development will serve as a buffer to
the SSSI and Conservation Area zones. It
will also provide a Nature Interpretation Centre to increase knowledge of the
environmental importance of the greater Sha Lo Tung Valley. Extensive landscaping is also proposed to
create a park like setting for the site.
The environmentally sensitive nature of the site will not have any
negative impacts on the Greenbelt Zone or the Sha Lo Tung OZP.
The temporary footbridge is located within the ‘Site
of Special Scientific Interest’ (SSSI) area of the Sha Lo Tung OZP.
The planning intention of this zone is to conserve and
protect the streamcourses and the freshwater marshes
which are important habitats for the breeding and development of rare species
and diverse community of dragonflies, for other aquatic and stream fauna such
as freshwater fishes and amphibians which are of special scientific interest.
It intends to deter human activities or developments with the Site of Special
Scientific Interest (SSSI).
The
temporary footbridge will only be in operation for approximately six months to
enable the construction of the fencing works at Lei Uk. The bridge is small in scale similar to what
may be encountered on a typical Hong Kong nature trail, and such trails are
permitted with conditions in the SSSI.
The
fencing works at Lei Uk are to be located in a
Village Type Development area of the Sha Lo Tung OZP.
The planning intention of this zone is to reflect existing
recognized and other villages, and to provide land considered suitable for
village expansion and reprovision of village houses
affected by Government projects. Land within this zone is primarily intended
for development of small houses by indigenous villages. It is also intended to
concentrate village type development within this zone for a more orderly
development pattern, efficient use of land and provision of infrastructure and
services. Selected community uses serving the needs of the villages and not
adversely affect the character of these villages and the adjacent ecologically
sensitive areas may be permitted on application to the Town Planning Board.
The fence
to be erected is generally in scale with residential developments and is not
considered to have any adverse impacts on this area.
The
majority of the road improvement works will occur within the Tai Po Outline
Zoning Plan No. S/P/23. The works will be
undertaken in the ‘Green Belt’ area.
The planning intention of this zone is primarily for
defining the limits of urban and sub-urban development areas by natural
features and to contain urban sprawl as well as to provide passive recreation
outlets. There is a general presumption against development within this zone.
The
improvement works will involve some re-alignment works, cutting and
filling. These works are generally in
accordance with the type of works permitted with or without conditions on
application to the Town Planning Board.
The
proposed Ecological Reserve covers areas zoned “V”, “GB”, “CA” and “SSSI”. In general, the proposed Ecological Reserve
complies with the planning intention for the area. However, it should be noted that while
“Nature Reserve” in the “CA” and “SSSI” zone requires planning permission from
the Town planning Board (the Board), such use is neither a Column 1 nor Column
2 use in the “V” zone and that would require rezoning application subject to
the approval of the Board.
It must
also be noted that changes to the Sha Lo Tung OZP will be required as a result
of the development. The proposed development project
would require approval of the Town Planning Board under s.12A and s.16 of the Town Planning Ordinance.
10.8
Landscape Impact
Assessment
10.8.1
Baseline Landscape Conditions
This Landscape Impact Assessment is focussed an area
within 500m of the Proposed Development Site and the Sha Lo Tung Road improvement
works. The landscape baseline study examines the potential impacts on the
Project areas and surrounding areas in terms of both the Landscape Character
Areas (LCAs) and the Landscape Resources (LRs).
The LCAs and LRs of the Study Area have been categorised according to
the presence of common elements. These
include factors such as:
·
Topography
and geological features;
·
Vegetation
type (both species and age);
·
Built
forms;
·
Evidence
of human modifications;
·
Land
use (past and present); and
·
Edges.
10.8.2
General Landscape Description
The site for the proposed development is on an
undulating series of grassy knolls, fringed with pockets of secondary
woodland. There are a number of grave
sites and many visible signs of hill fires.
The site has attractive views to the south west down to Tai Po and Tolo Harbour. To the
north, east and west, the site is surrounded by elevated peaks.
Geology
The Study Area lies on the
Tai Mo
Topography
To the northern boundary of the Study Area is the
ridge line of Ping Fung
To the west, is a ridge leading up to Cloudy Peak
which peaks at 440mPD.
The area surrounding the Development Site at Sha Lo
Tung contains a number of small ridges that exceed 220mPD to the south and west
of the Development Site. To the east the
site will be contained by the peaks and ridges that lie in a north easterly
direction at a height of over 300mPD.
Also as the Sha Lo Tung Road improvement works are located on the
western slopes of the ridge rising up to Sha Lo Tung, the visual envelope will
not extend further east past the immediate surroundings.
Drainage
The uplands of Cloudy Hill, Shek
Au
Vegetation
Vegetation within the Study area includes shrubs,
grasses, plantation areas and woodlands.
There are also some Fung Shui woodland areas
containing older trees. The majority of
the vegetation is contained in the more natural hill side areas, with some
pockets of vegetation found within the urban areas and the Tai Po Industrial
Estate.
Public
Open Spaces
There are numerous walking trails and picnic areas in
the Study Area, from Cloudy Peak to the west of the site, to the Pat Sin Leng Country Park to the north and east of the site.
Soil
The soils of the areas to the north of Ting Kok road are generally moist and rich in aluminium and
iron. The areas to the south of Ting Kok road are on a reclamation which consists of marine
silts and/or general fill.
10.8.3
Sensitivity and Magnitude to Change
To assess the potential impacts of the proposed
development on the LRs, it is necessary to understand
both the magnitude of change, and the sensitivity of the LRs
within the Study Area.
Sensitivity
The sensitivity for the landscape resources is
influenced by the quality of the Landscape Resource/Character Area. There are various factors that influence the
quality of a Landscape Resource/Character Area.
Those areas that appear unmodified or pristine are
rated highly; as are areas that may have been originally planted but have
achieved considerable age. Generally the
more pristine or natural a landscape or vegetation unit appears, the longer
this vegetation has been established, therefore the greater the
sensitivity. Similarly, modified
landscapes that are considered to have cultural values may also be assessed as
having a higher landscape values. This may
include elements that have a high cultural importance such as gardens,
significant open spaces, or meeting places that are of social importance, or
even built environments that have a conglomeration of highly valued cultural
elements.
The second factor that affects the perceived quality
of a Landscape Resource is its maturity.
Where the LR has extensive vegetation, this is generally a factor of
canopy height, with LRs that have a higher canopy
being regarded as more valuable. Other LRs may also have a high maturity level if they have been
in existence for a long period and have had little intervention from man made
elements. It is stressed that this is a
landscape evaluation, which may differ from an assessment that is based on
flora or ecological values.
Factors affecting the sensitivity for evaluation of
landscape are:
·
Quality
of LCAs and LRs;
·
Importance
and rarity of special landscape elements;
·
Ability
of the landscape to accommodate change;
·
Significance
of the landscape in the local and regional context, and;
·
Maturity
of the landscape.
The degree of sensitivity of the LCAs
and LRs is classified as follows:
·
High
– eg; important components or landscape of
particularly distinctive character susceptible to small changes;
·
Medium
– eg; a landscape of moderately valued
characteristics reasonably tolerant to change; and
·
Low –
eg; a relatively unimportant landscape which is able
to accommodate extensive change.
The magnitude of change to the LRs
is determined by measuring the extent to which the LRs
are changed by the development. This
compares the existing baseline conditions with those proposed after
development. The magnitude of change is classified as Negligible, Small,
Intermediate or Large depending on the affect the development will have on the
baseline LR.
Factors affecting the magnitude of change for
assessing landscape impacts are:
·
Compatibility
of the Proposed Development with the surrounding landscape, ie
how well will it fit with its surrounds;
·
Scale
of the development, ie how big is the development
relative to its surroundings, and;
·
Reversibility
of change, ie to how easily the changes to the
landscape can be reversed.
The magnitude of change is classified as follows:
·
Large
– notable change in the landscape characteristics over an extensive area
ranging to very intensive change over a more limited area;
·
Intermediate
– moderate changes to a local area;
·
Small
– changes to specific landscape components; and
·
Negligible
– no substantial changes to the baseline condition.
The baseline measurement is the measured area or
length of the existing landscape units within the landscape Study Area.
The baseline conditions will be compared with the
conditions that will occur during construction, immediately after development
and then after remediation works have occurred.
10.8.4
Impact Significance Assessment Matrix
The overall landscape impact will be a product of the
magnitude of change against the sensitivity of a particular landscape
resource.
Table 10.1 Impact Significance Assessment Matrix
|
Sensitivity |
|||
|
Low |
Medium |
High |
|
Magnitude of
Change |
Large |
Moderate |
Moderate/ Substantial |
Substantial |
Intermediate |
Slight/ Moderate |
Moderate |
Moderate/ Substantial |
|
Small |
Slight |
Slight/Moderate |
Moderate |
|
Negligible |
Negligible |
Negligible |
Negligible |
Table 10.1 will form the basis for the following
impact assessment of the LRs, LCAs
and VSRs identified within the Study Area.
10.8.5
Existing Landscape Character Areas and
Landscape Resources of the Study Area
A number of LRs have been
identified within the 500 metre Study Area and are mapped in Figure 10.1, with photographs shown in Figure 10.2 and 10.2a.
LR
1 Woodland
This LR is generally of high quality and Woodland is the
most commonly occurring LR within the Study Area, therefore, it is low in
rarity within the local and regional context.
The woodland areas are approximately 30 to 40 years old and they are
dominated by native tree species such as Schima superba, Schefflera heptaphylla, Ilex ficoidea and Castanopsis fissa.
The larger canopy species reached a height of 8-12 m and is generally a
mature landscape. Its relatively natural
state means this LR has a low ability to accommodate change. The sensitivity of this LR is considered High.
LR
2 Open Shrubland Areas
This LR consists of open grassy areas with scattered
groupings of shrubs of varying sizes.
Graves are also common within this LR and this LR is frequently
disturbed by hill fires during the grave sweeping festivals and has therefore
interrupted the natural succession of vegetation. This LR is dominated by grass species Miscanthus sinensis and
accompanied with some shrub species including Smilax china, Rhodomyrtus tomentosa, Rhaphiolepis indica and the fern species Dicranopteris linearis. This LR is generally of low – medium quality,
and is low in importance and rarity. It
has a low significance in local and regional contexts. The sensitivity of this LR is considered
Medium.
LR
3 Abandoned Agricultural Land
There are various areas of Abandoned
agricultural land found within the Study Area.
These include an area at the northeast of the Development Site, which
has regenerated from the paddy fields and has been invaded with grasses and
weed plants after cessation of agricultural activity. 103 plant species were recorded within the
habitat and they were dominated by Neyraudia arundinacea, Miscanthus sinensis, Ischaemum aristatum and the weedy climber Mikania micrantha. There are also areas of abandoned agricultural
land in the Fung Yuen Valley and to the east of Ha Hang. These areas vary from relatively dry areas,
to wetter marshy areas. There is a small
patch of marshy abandoned agricultural land located within the Development
Site. This LR is of importance in Hong Kong, with a low ability to accommodate
change. The sensitivity of this LR is
therefore considered High.
LR
4 Developed Area
The developed area comprises of generally hard built
elements such as extensive open areas, car parks, public toilets. All of these elements are constructed from
concrete, and do not complement the immediately
surrounding existing landscape, they are more in keeping with the Industrial
areas further to the south of the Study Area.
This LR is of low quality, low importance with a high ability to
accommodate change. The sensitivity of
this LR is considered Low.
LR
5 Stream
A number of natural streams occur within the Study
Area. The bed of the stream within the
SSSI area is rocky with medium-sized boulders.
Most of the streams are freely flowing and are generally in good
condition. There are also several
smaller seasonal streams within the Study Area.
Within the Development Site is a small seasonal stream that is known to
contain protected fish species, and is also of high landscape value. These streams are mostly of high landscape
quality and importance. They are locally
significant due to their relatively natural state. They also have a low ability to accommodate
change. The sensitivity of this LR is
considered High.
LR
6 Plantation
The plantation areas generally consist of younger
trees, usually less than twenty years old and are dominated by exotic
species. This LR is of low to medium
quality, however is not or rare or important and not locally or regionally significant. It has a medium ability to accommodate
change. This LR is considered to have a
Medium sensitivity.
LR
7 Roads
The roads within the Study Area are mostly located
within the Tai Po Industrial Area and include Ting Kok
Road. Fung Yuen Road and Sha Lo Tung
Road are the only roads extending to the north.
The roads are of low landscape quality, importance, rarity with a high
ability to accommodate change. This LR is considered to have a Low sensitivity.
LR
8 Villages
There are a number of villages within this area, the
largest being Fung Yuen. The village
generally consist of 3 storey villas, typical of Hong Kong’s New
Territories. The village areas are of
low landscape quality, importance, rarity with a high ability to accommodate
change. This LR is considered to have a
Low sensitivity.
LR
9 Abandoned Villages
There are two abandoned villages located within the
Sha Lo Tung area, Cheung Uk
and Lei Uk. Both of these villages have high
importance for both cultural and built heritage. They are rare within Hong Kong, and their
heritage value makes them locally significant.
Their sensitivity is considered to be high.
LR
10 Industrial Area
The industrial area consists of the buildings and
associated infrastructure located on the reclaimed area of land to the south of
Ting Kok Road.
This LR is of low landscape quality, importance, rarity with a high
ability to accommodate change. This area
is considered to have a Low sensitivity.
LR
11 Urban Development Area
This LR consists of the high-rise residential
development at Riviera Lodge to the north of Ting Kok
Road and a small portion of Alice Ho Mui Ling Nethersole Hospital.
The urban development areas are of low landscape quality, importance,
rarity with a high ability to accommodate change. This LR is considered to have a Low
sensitivity.
LR
12 Walking Trails and Picnic Areas
There are numerous walking trails located within the
study, most occurring in the northern portion of the Study Area. This LR
consists of simple gravel paths to hard paved trails. These trails are quite common within Hong Kong, however the popularity of hiking in Hong Kong makes
them locally significant. This LR is
considered to have a Medium sensitivity.
LR
13 Farmland
There are small pockets of active farmland located in
the Fung Yuen area. These are generally flat areas used for crop
cultivation. These areas are generally
of medium landscape quality, and are becoming increasingly rare in Hong Kong. They are considered to have a Medium
sensitivity.
LR
14 Fung Shui Woodlands
There are two major areas of Fung Shui
woodland areas, one located in the Fung Yuen area, and another adjacent to
Cheung Uk in Sha Lo Tung
valley area. These areas contain older
trees and vegetation that have a high cultural importance. This LR is considered to have a High
sensitivity.
Several landscape character areas (LCAs) have been identified within the Study Area. These areas, and their sensitivity, are
described below. The locations of the LCAs are mapped in Figure 10.3, with
photographs shown in Figure 10.4.
LCA1
Upland and Hillside Landscape
The Landscape Character is dominated by undulating
upland areas. There are patches of grassy hilltops that have been affected by
hill fires and have grave sites sporadically distributed around the area. In the lower valley areas, the vegetation is
dominated by the Secondary Woodlands and the Streams. The site is attractively framed by taller
hills to the north, east and west, and views to Tai Po are afforded in the
southern portion of the site. This LCA
is considered to have a High sensitivity.
LCA2
Fung Yuen Valley
This landscape comprises of scattered village houses
on the abandoned agricultural farm lands in the valley. The village houses are generally typical of
New Territories Villa style, most being 3 storeys tall. Ting Kok Road
borders this LCA to the south with the Tai Po Industrial Area beyond. The valley is framed by moderate to steeply
sloping vegetated slopes to the east, west and north of the valley. An approved residential development is
expected to be constructed in the northern portion of this LCA consisting of
approximately 8 20 – 24 storey towers and associated landscape. Construction has begun with road widening and
drainage works currently being undertaken.
This LCA is considered to have a Low sensitivity due to the proposed
changes in site conditions of the planned residential development,
however the development may be subject to amendment.
LCA3
Developed Area
The Developed area is dominated by the Tai Po
Industrial Estate contains numerous industrial buildings and
infrastructure. It is generally devoid
of soft landscape elements with the large buildings and roads dominating the
character of this area. This area has
been constructed on a reclamation and is therefore
generally flat. There are also some
residential areas on the northern side of Ting Kok
Road that are also included in this LCA. This LCA is considered to have a Low
sensitivity.
LCA4
Sha Lo Tung Valley
The Sha Lo Tung Valley is a gently undulating plateau
at approximately 180 mPD and contains a range of
vegetation types. These include sparse
grassland areas that have been affected by hillfires,
abandoned agricultural areas and clusters of remnant mature vegetation. This LCA also contains the two small villages
Chueng Uk
and Ping
10.8.6
Existing Trees
A Tree Survey has been conducted to record the
abundance, species name, location, trunk diameters and circumference, height,
crown spread, tree form, health condition and amenity value of the trees found
within the Development Site and along the Sha Lo Tung Road.
Development
Site
A total of 499 and 188 individual trees were found
within the Tree Survey Boundary and the Development Site, respectively, most of
which are native secondary woodland plants and dominated by a few native tree
species including Schima superba, Schefflera heptaphylla, Castanopsis fissa and Ilex ficoidea. None of the trees identified within the
Development Site are OVTs or of high amenity value or
tree species of conservation interest, except the Hairy Fruited Ormosia Tree Ormosia pachycarpa (recorded only in LR1) which is listed in
the ‘Rare and Precious Plants of Hong Kong’ and considered as tree species of
conservation interest. Most of the trees
have reached maturity but due to overcrowding they were recorded in poor to
fair tree form with low to medium amenity value.
Sha
Lo Tung Road Improvement
A total of 673 individual trees were found, most of
which are native secondary woodland plants and dominated by a few native tree
species including Schima superba, Schefflera heptaphylla and Cinnamomum camphora. Most
of the trees have reached maturity but due to overcrowding they were recorded
in poor to fair tree form with low to medium amenity value. None of the trees identified within the Sha
Lo Tung Road Improvement area are OVTs or of high
amenity value or tree species of conservation interest, except the Incense Tree Aquilaria sinensis (recorded in LRs 1,
2, 4 and 6) which is considered as tree species of conservation interest and
protected in the People’s Republic of
A detailed assessment of the potential impacts on the
existing trees is provided in Annex G.
10.8.7
Potential Sources of Impacts
The proposed development will create varying levels
of impact on the physical LRs and LCAs
within the Study Area at different stages of its lifetime.
During the Construction
Phase, potential impacts will result from the following:
·
Access
road construction;
·
Temporary
and permanent slope works;
·
Removal
of vegetation and site formation works;
·
Presence
of machinery and plant;
·
The
construction of the buildings and associated infrastructure, and
·
The
construction of the temporary footbridge and fence at Lei Uk.
During the Operation
Phase, no further Landscape Impacts are expected on the LRs
or LCAs.
However the new building structures will have an ongoing visual impact
during the operation phase and an ongoing impact on the LCAs
within the Study Area during the operation phase.
10.8.8
Nature and Magnitude of Landscape Impacts
before Mitigation during Construction Phase
The magnitude of the impacts, before implementation
of mitigation measures, on landscape resources and landscape character areas
that will occur in the Construction Phase are described below and tabulated in Table 10.3. All impacts are adverse unless otherwise
stated.
Landscape
Resources
LR
1 Woodland Areas
The construction associated with the Sha Lo Tung Road
improvement works will remove 0.17 ha, the cut slopes 0.03 ha and the
construction of the structures at the Development Site will only affect
approximately 0.025 ha of Woodland areas.
About 69 trees located within LR1 along Sha Lo Tung Road will be
affected by the Project. Approximately 374
and 300 trees located within LR1 at the Development Site and along Sha Lo Tung
Road respectively will be retained. The
LR1 is dominated by a few tree species including Schima superba, Schefflera
heptaphylla and Ilex ficoidea. Most of the trees have reached maturity but due
to overcrowding they were recorded in poor to fair tree form with low to medium
amenity value. The details regarding the
trees to be affected are identified in Annex G. The Project during construction and operation is not very compatible with this LR but
the total affected area is only 0.23 ha and given its abundance outside
the project areas, it will
expect to result in an Intermediate magnitude to change.
LR
2 Open Shrubland Areas
The construction works due to the development will
remove approximately 2.35 ha of this LR. The LR2 is dominated by fern species Dicranopteris
pedata and grass species Miscanthus sinensis and
accompanied by some shrub species including Smilax
china, Rhodomyrtus tomentosa,
Rhaphiolepis indica and Baeckea
frutescens and occasionally by scattered trees
including Schima superba
and hefflera heptaphylla. About
26 and 16 trees located within LR2 at the Development Site and along Sha Lo
Tung Road respectively will be affected by the Project. Approximately 39 and 8 trees located within
LR2 at the Development Site and along Sha Lo Tung Road respectively will be
retained. Most of the trees have reached
maturity but due to overcrowding they were recorded in poor to fair tree form
with low to medium amenity value. The
details regarding the trees to be affected are identified in Annex G. Despite the
Project not being compatible with this LR, given its abundance outside the
project areas, the magnitude
of change during construction and operation is considered Intermediate.
LR
3 Abandoned Agricultural Land
The construction works will not affect this LR, however, there will be some minor changes to this area
as a result of the construction of the temporary footbridge and fence. The temporary footbridge will be constructed
mainly from wooden materials and is considered moderately compatible with the
surrounding landscape. Due to the minor
scale of these works and reversibility of the changes, the magnitude of this
change is considered to be Small.
LR
4 Developed Area
The construction works associated with the Sha Lo
Tung Development Site and road improvement works will remove approximately 1.14
ha of this LR. The magnitude of this
change is considered Intermediate given the size of affected area.
LR
6 Plantation
Approximately 0.43 ha will be removed by the
construction works associated with the Sha Lo Tung Road Improvement, 0.24 ha as
a result of the road alignment, and 0.19 ha from the cut slopes. About 123 trees located within LR6 along Sha
Lo Tung Road will be affected by the Project.
The LR6 is mainly dominated by Schima superba and
Acacia confusa.
Most of the trees have reached maturity but due to overcrowding they
were recorded in poor to fair tree form with low to medium amenity value. The details regarding the trees to be affected
are identified in Annex G. The Project is not very compatible with this
LR but the total affected area is only 0.43 ha and given its abundance outside
the project areas, the
magnitude of change during construction and operation is considered Intermediate.
LR
7 Roads
Approximately 0.31 ha of the existing road will be
removed by the road improvement works.
This impact is considered to be beneficial. The magnitude of this change is considered Small given the small size of affected area and the compatibility
of the road improvement works with this LR.
There will not be any impacts on any other Landscape
Resources.
Landscape
Character Areas
LCA
1 Upland and Hillside Landscape
The construction works associated with the
Development Site and the road improvement works will remove approximately 2.86
ha of this LCA. These works are not
considered to be compatible with the surroundings, but the scale of the
development relative to the surroundings is considered to be small for the road
works and intermediate for the development site. The reversibility of the changes is
considered low as the works are considered permanent for the purposes of
assessment. However given the changes
will only affect 0.81% of this LCA within the study area, the magnitude of change
is considered to be Small.
LCA
2 Fung Yuen Valley
A small area of 0.52 ha of the Fung Yuen Valley LCA
will be removed by the road improvement works.
The Project is not considered to be compatible with this LCA but the
total affected area is only 0.52 ha and given its abundance outside
the project areas, the
magnitude of change is considered to be Small.
LCA
3 Developed Area
A very small area of 0.2 ha of this LCA will be
removed by the construction associated with the road improvement works. This magnitude of change is considered to be Small given the small size of affected area and the
compatibility of the road improvement works with this LCA.
LCA 4 Sha Lo Tung Valley
An almost insignificant area of 0.02 ha of the Sha Lo
Tung Valley LCA will be removed by the construction of the temporary footbridge
(which will be removed after not more than 3 months) in this LCA. The temporary footbridge will be constructed mainly from wooden
materials and is considered moderately compatible with the surrounding landscape
character. This magnitude of change is
considered to be Small.
10.8.9
Impacts on Existing Trees
Development
Site
Of the 499 trees recorded on the Tree Survey Boundary
including 188 trees within the Development Site, 35 (excluded two dead trees) will
be felled and 462 retained. The tree
species of conservation interest Hairy Fruited Ormosia
Tree Ormosia pachycarpa is
recommended to be retained. None of the
trees proposed to be felled within the Development Site are OVTs
or of high amenity value or of conservation interest.
Sha
Lo Tung Road Improvement
Of the 673 trees recorded along Sha lo Tung Road, 301
will be felled, 368 retained and 4 transplanted to non-impacted areas. None of the trees proposed to be felled
within the Sha Lo Tung Road Improvement area are OVTs
or of high amenity value or of conservation interest. The plant species of conservation interest
Incense Tree Aquilaria
sinensis is either recommended to be retained (16
individuals) or transplanted (4 individuals) to a non-impacted area.
The details on trees to be retained and felled in
contained within Annex G.
10.8.10
Nature and Magnitude of Landscape Impacts
before Mitigation during Operation Phase
There will be no additional impacts on any of the LRs or LCAs during the operation
of the Project, but there will be continuing impacts on the LCAs
and the residual LR impacts during the operation phase.
10.9
Landscape
Mitigation Measures
The landscape mitigation measures proposed will be
implemented progressively throughout the construction of the Proposed
Development to reduce the potential impacts on the existing LRs
and LCAs.
These measures will reduce the landscape impacts during both
construction and operation.
Table 10.2 Proposed
Design and Construction Phase Landscape and Visual Mitigation Measures
ID No. |
Landscape and Visual Mitigation
Measure |
Funding Agency |
Implementation Agency |
DM1 |
Design of Structures. The structures shown in the photomontages
are to illustrate the mass of the structures only. During the design phase of the development,
architectural features such as the, eaves, cladding, materials and finishes
etc. will be detailed. All of these
elements will greatly improve the appearance of the structures. Built structures will utilise appropriate
designs to complement the surrounding landscape, including a stepped form
that respects the site contours. |
Developer |
Design Team |
DM2 |
Colours.
Colours for the structures can be used to complement the surrounding
area. Lighter colours such as shades
of light grey, off-white and light brown may be utilised to reduce the
visibility of the structures. |
Developer |
Design Team |
DM3 |
Green Roofs.
Green roofs and vertical greening shall be designed and constructed to
integrate the new buildings into the surrounding environment. |
Developer |
Design Team |
CM1 |
Car Park Tree Planting. Advanced trees are to be planted to provide
shade to the car park areas and to reduce the mass of the paved areas. |
Developer |
Contractor |
CM2 |
Retention of Existing Trees. Existing trees without conflict with the
building structures will be retained to reduce impacts on the site. |
Developer |
Contractor |
CM3 |
Compensatory Planting. Where vegetation must be removed, the felled
trees within the Development Site and along Sha Lo Tung Road will be
compensated with new planting tree numbers at a
ratio of minimum 3:1 (1). |
Developer |
Contractor |
CM4 |
Columbarium Courtyard Plantings. The internal courtyards and areas
surrounding the new development will be landscaped to integrate the buildings
into the landscape. |
Developer |
Contractor |
CM5 |
Open Grassland and Lawn Areas. Areas of open grassland/lawns will be
created to provide areas for passive recreation and to complement the
surrounding grassland areas. |
Developer |
Contractor |
CM6 |
Buffer Planting. Trees and shrubs will be planted
around much of the site boundaries to screen the development and help
integrate the development into the surrounding landscape. |
Developer |
Contractor |
CM7 |
Stream Creation.
Streams containing pools and riffles will be created to create a
natural and harmonious landscape within the development. It must be noted that these features will
not be connected in any way to the natural stream bordering the site. |
Developer |
Contractor |
CM8 |
Early Planting Works. New plantings are to be installed in
available and formed lands during the construction works to reduce landscape
impacts. |
Developer |
Contractor |
CM9 |
Transplantation of Plants. In addition, plant materials that are in conflict with the development, that are in
suitably good condition and of ecological value will also be transplanted. |
Developer |
Contractor |
CM10 |
Soil Stabilisation and
Embankment Planting. During the design
process a soil stabilisation and embankment planting strategy should ensure
that land affected by slope excavation can be replanted. Soil preparation and the selection and
provision of suitable growing medium is to be
completed in accordance with the relevant best practice guidelines. |
Developer |
Contractor |
CM11 |
Cut Stabilisation Areas of
cut to be stabilized for operational requirements. Materials and finishes of stabilization to
be selected to complement the surrounding landscape. All landscape stabilisation measures must
conform to GEO 1/2000 – Technical Guidelines on
Landscape Treatment and Bio-engineering of Man-made Slopes and Retaining
Walls. |
Developer |
Contractor |
CM12 |
Colour of Site
Hoardings. In order to mitigate the
visual impact of these temporary hoardings, it is recommended that the
hoardings be erected at a uniform height, with a uniform colour that
complements the existing landscape. |
Developer |
Contractor |
DM = Design Measures (to be
undertaken prior to construction), CM = Construction Measure (to be carried
out during construction). Note: (1) The
exact number of compensatory trees will subject to the results of Tree
Felling Application. |
The landscape mitigation measures are shown in Figures 10.5a, b, c and d. Additional
good site practices are also recommended to mitigate the impacts:
·
Cultivation of areas impacted during
construction - Areas
impacted during the construction phase that are not required during the
operation phase, are to be cultivated to a depth of 300mm in accordance with
accepted Hong Kong practice and guidelines. The cultivation shall involve
ripping of compacted soil by mechanical means.
Great care must be taken to avoid any run-off into the existing streams.
Therefore this mitigation measure is not to be adopted in areas sloping towards
any existing watercourses.
·
Quality control of imported materials - Appropriate quality control measures
are to be used to ensure that all imported materials including but not limited
to soils, mulches, plants etc. are to be free of pests and contaminants that
may adversely affect the surrounding environment. All landscape construction works are to be
supervised by suitably trained professionals.
Programme
of Implementation of Landscape and Visual Mitigation Measures
Design phase mitigation measures above will be
carried out before construction, and Construction phase mitigation will be
carried out during the construction phase of the project.
A Landscape Master Plan has been prepared (Figure 10.5a) which shows the landscape that will be
installed as part of the development.
The Landscape and Visual Mitigation Plan also identifies specific
mitigation measures for the Development Site, the Ecological Reserve and the
Sha Lo Tung Road improvement works.
10.9.2
Prediction of Significance of Landscape
Impacts
The potential significance of the landscape impacts
during the construction and operation phases, before and after mitigation, are
provided below in Table 10.3 and
mapped in Figures 10.6 – 10.8. This assessment follows the methodology
outlined above and assumes that the appropriate mitigation measures identified
in Table 10.2 above will be
implemented, and that the full mitigating effect of the soft landscape
mitigation measures will be realised after ten years. The residual landscape impacts during the
construction and operation phases, before and after mitigation, are mapped in Figures 10.9 – 10.11. Photomontages of the proposed development
before and after mitigation are illustrated in Figures 10.18 –
10.27.
Construction Phase
In the construction phase, after the implementation
of the proposed mitigation measures, there will still be some adverse residual
landscape impacts as described below.
There will be no Adverse residual landscape impacts
of ‘Substantial’ significance experienced by any of the landscape resources.
Adverse residual landscape impacts of ‘Moderate’
significance will be experienced by the following landscape resources:
LR1 – Woodland.
The construction works on the Development Site and road improvement
works will require the removal of approximately 0.225 ha of vegetation within
the woodland. The trees lost can be
replaced within the site. This temporary
loss will create a ‘Moderate’ impact during construction.
LR2
– Open Shrubland. The site
formation works on the Development Site will result in the loss of
approximately 2.35 ha of this LR. This temporary
loss will create a ‘Moderate’ impact during construction.
LR6 – Plantation.
The site formation associated with the road improvement works will
result in the loss of trees, and 0.43ha of this LR will lost. However, these trees are all exotic plantation
species that are fast growing and easily replaced. The temporary loss of this vegetation will
create a ‘Moderate’ impact during construction.
LCA1
– Upland and Hillside Landscape. The site
formation works and construction works associated with the Sha Lo Tung Road
improvement and the Development Site will introduce a man-modified element into
the area that contrasts with the naturalness of this LCA. Approximately 2.86 ha of this LCA will be
changed during construction. This
temporary period will create a ‘Moderate’ impact during construction.
LCA4
– Sha Lo Tung Valley. Only a very small area of 0.02 ha of this LCA will be affected, which is
a small magnitude of change. However, due to the high sensitivity of this LCA
this impact is considered to be ‘Moderate’.
Adverse residual landscape impacts of ‘Slight’
significance will be experienced by the following landscape resources and
character areas:
LR3 – Abandoned Agricultural
Land. A very small area of this LR will be affected by the
construction of the temporary footbridge and the fencing works at Lei Uk village. This
will result in a ‘Slight’ impact to this LR during construction.
LR4
– Developed Area. The construction on the Development Site and the
Sha Lo Tung Road improvement works will affect 1.14 ha of this LR, which is
considered ‘Slight’. However due to the low quality of this LR this is not
considered an ‘adverse’ impact. In addition, this LR will be replaced by a new
development of higher quality.
LCA2
Fung Yuen Valley. Approximately 0.52 ha of this LR will be
affected by the Sha Lo Tung Road improvement works. This is considered a
‘Slight’ impact due to the low sensitivity and small magnitude of change.
All other construction phase impacts will be of
“Negligible” significance.
Operation Phase
There will be no additional impacts on any of the
Landscape Resources or Character Areas during the operation phase. Following the implementation of the
mitigation measures, the landscape impacts will be as follows:
There will be no adverse residual landscape impacts
of ‘Substantial’ significance experienced by any of the landscape resources or
landscape character areas.
LCA4 Sha Lo Tung Valley - This LR will still experience a
‘Moderate’ residual impact at Day 1 of operation. This will reduce to ‘Slight’
at Year 10 of operation.
Adverse residual landscape impacts of ‘Slight’
significance will be experienced by the following landscape resources and
character areas at Day 1 of operation:
LR1 – Woodland, and LR6 - Plantation The extensive plantings shown in Figure 10.5 will largely mitigate the loss of these Landscape
Resources, resulting in a slight impact at Day 1 of operation. As this
vegetation matures, these impacts will reduce to ‘Negligible’ at year 10 of
operation for LR6, however a ‘Slight’ impact will remain for LR1.
LR2
– Open Shrubland. As with LRs 1 and 6, the extensive plantings
will largely mitigate the impacts on this LR.
However, on an area basis, this will not be fully mitigated and there
will be a ‘Slight’ impact at Year 10 of operation.
LR3 – Abandoned Agricultural
Land. With the removal of the temporary footbridge and
adoption of the recommended mitigation measures, there will be a ‘Slight’
impact to this LR at Day 1 of operation, reducing to ‘Negligible’ at Year 10.
LCA1
Upland and Hillside Landscape. The extensive plantings and landscape
improvements shown in Figure 10.5
will also largely mitigate the impacts of this LCA, reducing to Slight at Day 1
of operation. The Development Site will
continue to have an impact on this LCA for the life of the project, however it
is only considered to be ‘Slight’.
All other impacts will be of ‘Negligible’
significance.
Table 10.3 Residual
Landscape Impacts
ID No. |
Landscape
Resource / Landscape Character |
Sensitivity (Low, Medium,
High) |
Existing area within the study boundary (ha)/(km) |
Area affected by the project |
Percentage (%) of area affected |
Magnitude of Change BEFORE
Mitigation (Negligible, Small,
Intermediate, Large) |
Impact Significance BEFORE Mitigation (Negligible, Slight, Moderate,
Substantial) |
Recommended Mitigation Measures |
Residual Impact Significance Threshold AFTER Mitigation (Negligible,
Slight, Moderate, Substantial) |
||||
Construction |
Operation |
||||||||||||
Construction |
Operation |
Construction |
Operation |
|
DAY 1 |
YEAR 10 |
|||||||
LR1 |
Woodland |
High |
119.24 ha |
0.225 ha |
0.19% |
Intermediate |
Intermediate |
Moderate |
Moderate |
CM2, 3, 6, 8, 9 |
Moderate |
Slight |
Slight |
LR2 |
Open Shrubland Areas |
Medium |
236.53 ha |
2.35 ha |
0.10 % |
Intermediate |
Intermediate |
Moderate |
Moderate |
CM6, 8, 9 |
Moderate |
Slight |
Slight |
LR3 |
Abandoned
Agricultural Areas |
High |
43.90 ha |
0.005ha |
1.14% |
Small |
Small |
Slight |
Slight |
CM2, 3, 8, 9 |
Slight |
Slight |
Negligible |
LR4 |
Developed Area |
Low |
13.70 ha |
1.14 ha |
8.3% |
Intermediate |
Intermediate |
Slight |
Slight |
DM1, 2, CM1 ,2 ,3,
8, 12 |
Slight |
Negligible |
Negligible |
LR5 |
Natural Stream |
High |
0.67 ha |
Nil |
N/A |
Negligible |
Negligible |
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
Negligible |
LR6 |
Plantation |
Medium |
17.75 ha |
0.43 ha |
2.42% |
Intermediate |
Intermediate |
Moderate |
Moderate |
CM2, 3, 6, 8, 9 |
Moderate |
Slight |
Negligible |
LR7 |
Roads |
Low |
11.84 ha |
0.31 ha |
2.62% |
Small |
Small |
Slight |
Negligible |
CM11, 12 |
Slight |
Negligible |
Negligible |
LR8 |
Villages |
Low |
7.64 ha |
Nil |
N/A |
Negligible |
Negligible |
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
Negligible |
LR9 |
Abandoned Villages |
High |
0.70 ha |
Nil |
N/A |
Negligible |
Negligible |
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
Negligible |
LR10 |
Industrial Areas |
Low |
40.30 ha |
Nil |
N/A |
Negligible |
Negligible |
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
Negligible |
LR11 |
Urban Development
Area |
Low |
2.0986 ha |
Nil |
N/A |
Negligible |
Negligible |
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
Negligible |
LR12 |
Walking Trails and
Picnic Areas |
Medium |
106.77 km |
Nil |
N/A |
Negligible |
Negligible |
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
Negligible |
LR13 |
Farmland |
Medium |
1.62 ha |
Nil |
N/A |
Negligible |
Negligible |
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
Negligible |
LR14 |
Fung Shui Woodlands |
High |
3.25 ha |
Nil |
N/A |
Negligible |
Negligible |
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
Negligible |
LCA1 |
Upland and
Hillside Landscape |
High |
339.61 ha |
2.86 ha |
0.84% |
Small |
Small |
Moderate |
Moderate |
All |
Moderate |
Slight |
Slight |
LCA2 |
Fung Yuen Valley |
Low |
40.21 ha |
0.52 ha |
1.3% |
Small |
Small |
Slight |
Slight |
DM1, 2, CM2, 6, 8 |
Slight |
Negligible |
Negligible |
LCA3 |
Developed Area |
Low |
68.62 ha |
0.02 ha |
0.02% |
Small |
Small |
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
Negligible |
LCA4 |
Sha Lo Tung Valley |
High |
50.75 ha |
0.02 ha |
2.14% |
Small |
Small |
Moderate |
Moderate |
DM1, 2, CM1, 2, 3,
8, 12 |
Moderate |
Moderate |
Slight |
10.10
Visual Impact Assessment
10.10.1
Introduction
The
following tasks were undertaken for the visual impact assessment.
Define the view shed that
would be potentially impacted by the Project and map the areas of visual impact
- Geographical
Information System (GIS) software was utilised to determine areas that could potentially
see the development during construction and operation. This GIS view shed analysis was based solely
on topography and did not take into account the screening potential of
vegetation, which would further reduce the actual view shed. The GIS view shed analysis also mapped the
visibility of the development from roads and houses.
Assess indicative view
points as a means of assessing the visual impact on the broader landscape -
Visually Sensitive
Receiver (VSR) view points around the development, have been selected as
indicative of the range of views from accessible locations within the view
shed. Photomontages have been prepared
to show the existing landscape and the landscape with the development at the
key VSRs.
Discuss visual mitigation measures - measures (if required) that will reduce any potential visual impacts
have been identified. This may include
planting and recommendations for material and finishes. These measures will also help improve the
overall amenity of the Project. Residual
impacts are also discussed.
10.10.2
Potential Sources of Visual Impacts
The sources of visual impact during construction will
be those identified above in Section
10.8.7. During operation, the
continuing physical presence of the new buildings and cut slopes along Sha Lo
Tung road will generate a visual impact.
The works described are all contained within the Sha Lo Tung road
improvement works and the Development Site.
There will also be minor works in the Ecological Reserve, including the
construction of a temporary footbridge, and a visually transparent fence at Lei
Uk village.
All of these elements are considered in this assessment.
10.10.3
Visual Envelope Determination and Areas of
Potential Visual Impact
The visual
impact assessment is informed by an understanding of the existing visual
qualities within the region that can be visually affected by a
development. This area is referred to as
the visual envelope.
Defining an appropriate visual envelope is the
starting point to understanding the visual impacts of a development as the area
of the visual envelope will vary depending on the nature and scale of the
proposed development. The larger a
development the greater the visual envelope as it may be visually apparent for
a greater distance. Once the visual
envelope is established, locations can be identified within the visual envelope that are either particularly sensitive or
indicative of the visual impact for a number of locations.
The proposed Multi-Cultural
Education Retreat and the Nature Interpretation Centre are the major visual element of the proposed
development and may visually impact on the surrounding VSRs. As the viewer moves further away from these
structures the visual impact decreases until it is no longer visible.
10.10.4
General Visual Envelope based on Site
Topography
The proposed development will be visible from some
surrounding areas and therefore an analysis of these areas and the extent of
the potential visual impact is to be assessed. The visual envelope has been determined by a
GIS analysis of the area within which the proposed development will be seen.
Figure 10.12 shows those areas that will potentially
be able to see the development. It also
should be noted that the GIS analysis only accounts for the terrain, and does
not allow for vegetation or built forms.
Therefore, the actual visual envelope will be smaller than shown.
The layouts of the buildings have undergone a
rigorous design process to reduce the heights and visibility of the
development, whilst maintaining the minimum footprint size and impact.
To the northern boundary of the visual envelope will
extend to the ridge line of Ping Fung
To the west, the visual envelope is contained by the
ridge leading up to Cloudy Peak which peaks at 440mPD.
The siting of the
Development Site at Sha Lo Tung will effectively contain the visual envelope to
the south within the site area. There
are a number of small ridges that exceed 220mPD to the south and west of the
Development Site which prevents views to the site from areas below,
particularly Fung Yuen. The road works
will be visible from this location, however the
southern extents of the visual envelope created by the road works will be
contained by the industrial developments at Tai Po Industrial Estate.
The visual envelope to the east will be contained by
the peaks and ridges that lie in a north easterly direction at a height of over
300mPD. Also as the Sha Lo Tung Road
improvement works are located on the western slopes of the ridge rising up to
Sha Lo Tung, the visual envelope will not extend further east past the
immediate surroundings.
10.10.5
Existing Visual Amenity of the Site and
Surrounds
The visual amenity of the site varies widely. At the intersection of Sha Lo Tung Road with
Ting Kok Road, the view is dominated by the
make-shift car repair and storage facilities and the busy traffic on Ting Kok Road. Sha Lo
Tung Road then begins to meander at an increasing slope and quickly becomes
surrounded in vegetation. Existing cut
slope stabilisation is visible. The
existing Water Supplies Department storage facilities are also visible on the
right. As the right rises further
towards the Development Site, the vegetation becomes more sparse providing
views across Fung Yuen valley and south to Tai Po. The Development Site is set in a largely
natural location with some development visible being the existing car park,
sitting out area and toilet facilities.
The site contains several grassy knolls that have been regularly
affected by hill fires with some scattered graves also visible in the
surrounding area. The site is framed by
areas of woodland with the steeply sloping peaks to the north, east and west. The site generally evokes a calm serene
visual environment with dramatic views of the hills to the north and the sea to
the south.
10.10.6
Visual Envelope Determination based on the
Parameters of Human Vision
In addition to the site analysis provided above, an
analysis of the parameters of human vision is also required to determine how
far the visual envelope will extend where there is no intervening topography or
man made elements.
In order to undertake this assessment, the components
of the project must be grouped. The
elements of the project that will potentially have the greatest visual envelope
are the Development Site and the Road Upgrade Works. Both have very different physical dimensions
and will have potentially different visual envelopes.
10.10.7
Horizontal Field of View
The central field of vision for most people covers an
angle of between 50° and 60°. Within
this angle, both eyes observe an object simultaneously. This creates a central field of greater
magnitude than that possible by each eye separately. This central field of vision is termed the
'binocular field' and within this field images are sharp, depth perception
occurs and colour discrimination is possible.
These physical parameters are illustrated in Figure 10.12a.
The visual impact of a development will vary
according to the proportion in which a development impacts on the central field
of vision. Developments, which take up
less that 5% of the central binocular field, are usually indistinguishable in
most landscapes (5% of 50° = 2.5°).
The Development Site is comprised of a several new
buildings, the longest dimension being the length of the Multi-Cultural Education Retreat, which is approximately 40m.
In assessing the visual impact of the Development
Site it is therefore assumed that the largest horizontal component is the Multi-Cultural Education Retreat, which based on the current preferred design is
approximately 40 metres wide.
Table 10.4 Visual Impact Based on the Horizontal Field of View
Horizontal Field of
View |
Impact |
Distance from an
Observer to a 100m wide reclamation |
<2.5° of view |
The
development will take up less than 5% of the central field of view. The development, unless particularly
conspicuous against the background, will not intrude significantly into the
view. The extent of the vertical
angle will also affect the visual impact. |
|
2.5° – 30° of view |
The development may be noticeable and its degree of
visual intrusion will depend greatly on its ability to blend in with its
surroundings. |
200m –
2.3km |
>30° of view |
Potentially visually dominant Developments that fill
more than 50% of the central field of vision will always be noticed and only
sympathetic treatments will mitigate visual effects. |
< 200m |
As shown in Table
10.4, these calculations suggest that the impact of a 100 m wide building
would reduce to indistinguishable at about 2.3 km, as it would form less than
5% or 2.5° of the horizontal field of view.
Due to the very long narrow nature of the road improvement works, an
analysis of the horizontal field of view is not appropriate as the vertical
elevations of the works will disappear well before the horizontal calculations
would suggest.
10.10.8
Vertical Field of View
A similar analysis can be undertaken based upon the
vertical field of view for human vision.
As can be seen in the Figure 10.12a
the typical line of sight is considered horizontal or 0°. A person’s natural or normal line of sight is
normally a 10° cone of view below the horizontal and, if sitting, approximately
15°.
Objects which take up 5% of this cone of view (5% of
10° = 0.5°) would only take up a small proportion of the vertical field of
view, and are only visible when one focuses on them directly. Objects that take up such a small proportion
of the vertical view cone are not dominant, nor do they create a significant
change to the existing environment when such short objects are placed within a
disturbed or man-modified landscape.
The largest vertical dimension for the Development
Site will be the height of the Multi-Cultural
Education Retreat, which is
approximately 13.3 metres. For the road
improvement works the tallest vertical elements will be the large cut slopes
above and below the road which may be up to 8m in overall height.
Table 10.9 shows the relationship between impact and the
proportion that the development occupies within the vertical line of sight.
Table 10.5 Visual Impact Based on
Vertical Field of View
Vertical Line |
Impact |
Distance from an Observer to a 13.3m Tall
Building |
Distance from an Observer to an 8m Cut Slope |
< 0.5° of vertical angle |
Indistinguishable A thin line in the
landscape. |
> 1.5 km |
> 900m |
0.5° – 2.5° of vertical angle |
Potentially noticeable The degree of visual
intrusion will depend on the development’s ability to blend in with the
surroundings. |
300m – 1.5 km |
180m – 900m |
> 2.5° of vertical angle |
Visually evident Usually visible,
however the degree of visual intrusion will depend of the width of the
object and its placement within the landscape. |
< 300m |
< 180m |
These calculations suggest distances at which the
magnitude of visual impact of the tallest building and largest cut slopes will
reduce with distance. At distances
greater than 1.5km, a fully visible 13.3 m tall building and would be an
indistinguishable element within the landscape.
Similarly, an 8m tall cut slope will be indistinguishable at 900m.
10.10.9
Determining the Visual Extent of Impact
Generally, the more conservative,
or worse-case distances form the basis for the assessment of visual
impacts. Therefore for this development
the greater impacts would be associated with the vertical field of view. It is therefore proposed to use the vertical
field of view and extend the visual envelope to 2.3 km for the Development Site
and 900m for the road improvement works.
10.10.10
GIS Analysis
A GIS view shed analysis has identified those areas
that can potentially be visually impacted by the project (see Figure 10.12). Such analysis is based on topography only,
and shows those areas that would be screened by intervening hills etc. It does not take into account intervening
vegetation or buildings, nor does it take into account small variations in
topography, such as road cuttings.
Therefore it is a conservative assessment of those areas that may be
potentially able to view the project.
10.10.11
Atmospheric Factors Which Will Affect
Visual Impact
Many climatic conditions result in changes to
visibility. For example, sea haze will
alter the visibility of the project. The
diminution of visual clarity bought about by atmospheric conditions also
increases with distance.
Cloud Cover
Cloudy days can also reduce the visibility of the development. During site inspections of similar facilities it was apparent that a backdrop of grey cloud reduced the visual impact of the structures. Full cloud cover also reduced the apparent contrast on elements that extend above the landscape backdrop and as these elements were neither strongly shadowed nor reflective.
Figure 10.12b shows that in Hong Kong, for much of the
year the percentage of cloud cover exceeds 50%.
Rainfall
The effect that rainfall has on visibility can be measured in two ways. Firstly, the event of falling rain reduces visibility as the water droplets obscure vision. This varies greatly depending on the heaviness of the precipitation, but even light rain obscures distant objects greatly. Secondly, the event of rain, particularly sustained rain periods, reduces visitor numbers. Therefore, the visual impact is reduced on those days as lesser viewers are visiting the area and looking at the development.
Figure 10.12b also shows that during the wet season,
particularly from May through September, Hong Kong receives on average
approximately 10mm of rain per day.
These rain events can reduce visibility.
Reduced Visibility
The Hong Kong Observatory noted that in 2008 there
were a total of 1,951 hours of reduced visibility in Hong Kong. Reduced visibility is defined as:
Reduced visibility refers to
visibility below 8 kilometres when there is no fog, mist, or precipitation.
On days when reduced visibility is being experienced in Hong Kong, the
maximum view shed any development will reduce to less than 8 kilometres.
Assessment
Scenarios
Whilst the above describes some of the climatic conditions that reduce the visibility of the project, the following assessment is based on a worse case impact scenario on visual quality assuming perfectly clear viewing conditions. Mitigation measures are proposed to reduce these impacts.
10.10.12
VSR Assessment Methodology
The
following factors have been considered in the visual impact assessment.
VSR Sensitivity
The first set of criteria relate to the sensitivity of the VSRs. They include:
·
Value
and quality of existing views;
·
Type
and estimated number of receiver population;
·
Availability
and amenity of alternative views;
·
Duration
of frequency of view; and
·
Degree
of visibility.
The
views available to the identified VSRs were rated in
accordance with their sensitivity using high, medium or low and are defined as
follows:
·
High
i.
The nature of the viewer groups who expect
a high degree of control over their immediate environment; and
ii.
The viewer groups are in close proximity to
the Proposed Development.
·
Medium
iii.
The nature of the viewer groups who have
some degree of control over their immediate environment, eg
people in transit.
·
Low
iv.
The nature of the viewer groups does not
expect a high degree of control over their immediate environment.
It should be noted that the above only provides
guidance, and each VSR regardless of type has been assessed according to its
specific circumstances.
The sensitivity of the existing VSRs
is shown in Figure 10.13 and Table 10.6 below:
Table
10.6 Sensitivity of VSRs
VSR
Type &
ID. |
Key
Visually Sensitive Receiver (VSR) |
Value
and quality of existing views; |
Type
and estimated number of receiver population; |
Availability
and amenity of alternative views; |
Duration
of frequency of view |
Degree
of visibility |
Sensitivity (Low,
Medium, High) |
R1 |
Hikers on the Wilson trail west of project areas |
High quality views across a natural landscape to the
east, with development visible to the south east |
Few |
High, a range of views are available. |
Short term views that change as the VSR moves along
the path. |
High |
High |
R2 |
Cyclists along Ting Kok
Road |
Low - Medium quality views dominated by Ting Kok Road |
Few |
Medium, the views is generally focussed along the
road with occasional views of the surroundings. |
Very short term views as the VSR moves along the bike
path. |
Low |
Medium |
R3 |
Hikers within the Pat Sing Leng
Country Park west of site |
High quality views across a natural landscape to the
east, with development visible to the south |
Very Few |
Medium, the views is focused to the east. |
Short term views that change as the VSR moves along
the path. |
High |
High |
R4 |
Visitors to Chueng Uk Village |
High quality views ranging from close range vegetation
to long distance views of surrounding landscape. |
Very Few |
High, there are a wide variety of views from the
Cheung Uk village area. |
Short term views that change as the VSR moves around
the area. |
Medium |
Medium |
R5 |
Visitors to Lei Uk Village |
High quality views ranging from close range
vegetation to long distance views of surrounding landscape. |
Very Few |
High, there are a wide variety of views from the Lei Uk village area. |
Short term views that change as the VSR moves around the
area. |
Medium |
Medium |
R6 |
Hikers on path from Fung Yuen to Sha Lo Tung Road |
Medium quality views across the Fung Yuen valley |
Few |
Medium, the view is generally focussed on the valley
below. |
Short term views that change as the VSR moves along
the path. |
Medium |
Medium |
R7 |
Hikers walk in Fung Yuen Valley |
Medium quality views across the Fung Yuen valley |
Very Few |
Medium, the view is generally focussed on the valley
below. |
Short term views that change as the VSR moves along
the path. |
Medium |
Medium |
R8 |
Hikers on Wilson Trail north of project areas |
High quality views of a dramatic landscape |
Few |
Medium, the view is generally focussed to the south. |
Short term views that change as the VSR moves along
the path. |
High |
High |
R9 |
Hikers in Pat Sin Leng
Country Park North of project areas |
High quality views of a dramatic landscape |
Very Few |
Medium, the view is generally focussed to the south. |
Short term views that change as the VSR moves along
the path. |
High |
High |
R10 |
Hikers in Pat Sin Leng
Country Park East of project areas |
Assumed to be high (trails could not be accessed) |
Very Few |
Assumed to be medium |
Short term views that change as the VSR moves along
the path. |
High |
High |
H1 |
Residents of Fu Heng Estate |
High quality views across a mix of developed and
natural landscapes |
Many |
Low, views generally focussed towards the orientation
of the premises |
Long frequent views |
High |
High |
H2 |
Residents in Pinehill, Yue Kok Tsuen,
Tit Mei Tsai |
High quality views across a mix of developed and
natural landscapes |
Many |
Low, views generally focussed towards the orientation
of the premises |
Long frequent views |
High |
High |
H3 |
Residents at Fung Yuen Village |
High quality views of the surrounding valley |
Many |
Low, views generally focussed towards the orientation
of the premises |
Long frequent views |
High |
High |
H4 |
Residents of new Fung Yuen development |
High quality views of the surrounding valley |
Many |
Low, views generally focussed towards the orientation
of the premises |
Long frequent views |
High |
High |
H5 |
Residents in Ha Hang |
Medium quality views of Tai Po and surrounds |
Many |
Low, views generally focussed towards the orientation
of the premises |
Long frequent views |
High |
High |
H6 |
Residents in Casa Marina, Forest Hill, Richwood Park,
Typhoon Place |
Medium quality views of Tai Po and surrounds |
Many |
Low, views generally focussed towards the orientation
of the premises |
Long frequent views |
High |
High |
H7 |
Residents in A Sha, Tsin
Lam, A |
Medium quality views of Tai Po and surrounds |
Few |
Low, views generally focussed towards the orientation
of the premises |
Long frequent views |
High |
High |
O1 |
Workers at Tai Po Industrial Estate |
Low quality views of surrounding industrial areas |
Many |
Low, views generally focussed towards the orientation
of the premises |
Medium term views |
Low |
Low |
O2 |
Workers at Hong Kong Institute of Education |
Medium quality views of surrounding developments with
some views of surrounding landscape |
Few |
Low, views generally focussed towards the orientation
of the premises |
Medium term views |
Low |
Low |
T1 |
Travellers along Ting Kok
Road |
Low - Medium quality views dominated by Ting Kok Road |
Many |
Medium, the views is generally focussed along the
road with occasional views of the surroundings. |
Very short term views as the VSR moves along the road |
Low |
Low |
T2 |
Travellers along Fung Yuen Road |
Medium quality views of village structures with
natural slopes to the north, east and west |
Few |
Medium, the views is generally focussed along the
road with occasional views of the surroundings. |
Very short term views as the VSR moves along the road |
Low |
Low |
T3 |
Travellers along Sha Lo Tung Rd |
Medium – high quality views of surrounding landscape
dispersed between roadside vegetation |
Few |
Low, views generally focussed on the road corridor |
Very short term views as the VSR moves along the road |
Low |
Medium |
10.10.13
Magnitude of Change
This set of criteria is related to the specific
details of the proposed development and how it relates to the existing
landscape and the visible magnitude of change it will cause. The criteria to be assessed are:
·
Compatibility
of the Proposed Development with the surrounding landscape;
·
Reversibility
of change;
·
Viewing
distance;
·
Scale
of the development;
·
Potential
blockage of view; and,
·
Duration
of impact under construction and operation phases.
The
magnitude of change to a view was rated as large,
intermediate, small or negligible and are defined as follows:
·
Large:
eg major change in view;
·
Intermediate:
eg moderate change in view;
·
Small:
eg minor change in view; and,
·
Negligible:
eg no discernible change in view.
The magnitude of change for each of the VSRs is shown in Table
10.7 below.
Table 10.7 Magnitude of change of VSRs
VSR Type & ID. |
Key Visually Sensitive Receiver (VSR) |
Compatibility of the Proposed Development with the surrounding
landscape |
Reversibility of change |
Viewing distance (m) |
Scale of the development |
Potential blockage of view |
Duration of Impact |
Magnitude of Change BEFORE Mitigation (Negligible, Small, Intermediate, Large) |
||
|
|
|
|
|
|
|
Construction |
Operation |
Construction |
Operation |
R1 |
Hikers on
the Wilson trail west of project areas |
Low, the
view of the site is generally natural |
Irreversible |
1000 |
Medium |
Low |
Temporary |
Permanent |
Intermediate |
Intermediate |
R2 |
Cyclists
along Ting Kok Road |
High, the
visible elements of the development (Sha Lo Tung Road improvement) and compatible
with Ting Kok Road |
Irreversible |
10-50 |
Medium |
Low |
Temporary |
Permanent |
Intermediate |
Intermediate |
R3 |
Hikers
within the Pat Sing Leng Country Park west of site |
Low, the
view of the site is generally natural |
Irreversible |
500 -
2300 |
Medium |
Low |
Temporary |
Permanent |
Large |
Large |
R4 |
Visitors
to Chueng Uk Village |
Medium
the surrounds are generally natural with some signs of development |
Irreversible |
200 |
Large |
Low |
Temporary |
Permanent |
Intermediate |
Intermediate |
R5 |
Visitors
to Lei Uk Village |
Medium
the surrounds are generally natural with some signs of development |
Irreversible |
200 |
Large |
Low |
Temporary |
Permanent |
Intermediate |
Intermediate |
R6 |
Hikers on
path from Fung Yuen to Sha Lo Tung Road |
Medium
the surrounds are generally natural with some signs of development |
Irreversible |
10-200 |
Small |
Low |
Temporary |
Permanent |
Intermediate |
Intermediate |
R7 |
Hikers
walk in Fung Yuen Valley |
Medium the
surrounds are generally natural with some signs of development |
Irreversible |
500-1000 |
Small |
Low |
Temporary |
Permanent |
Intermediate |
Intermediate |
R8 |
Hikers on
Wilson Trail north of project areas |
Low, the view
of the site is generally natural |
Irreversible |
1500 |
Medium |
Low |
Temporary |
Permanent |
Small |
Small |
R9 |
Hikers in
Pat Sin Leng Country Park North of project areas |
Low, the
view of the site is generally natural |
Irreversible |
700 |
Medium |
Low |
Temporary |
Permanent |
Small |
Small |
R10 |
Hikers in
Pat Sin Leng Country Park East of project areas |
Low, the
view of the site is generally natural |
Irreversible |
700 -
2000 |
Medium |
Low |
Temporary |
Permanent |
Small |
Small |
H1 |
Residents
of Fu Heng Estate |
Medium,
there are both natural and built forms visible |
Irreversible |
2000 |
Medium |
Low |
Temporary |
Permanent |
Small |
Small |
H2 |
Residents
in Pinehill, Yue Kok Tsuen, Tit Mei Tsai |
Medium,
there are both natural and built forms visible |
Irreversible |
200 -
1000 |
Medium |
Low |
Temporary |
Permanent |
Small |
Small |
H3 |
Residents
at Fung Yuen Village |
Medium,
there are both natural and built forms visible |
Irreversible |
300 |
Medium |
Low |
Temporary |
Permanent |
Small |
Small |
H4 |
Residents
of new Fung Yuen development |
Medium,
there are both natural and built forms visible |
Irreversible |
300 |
Medium |
Low |
Temporary |
Permanent |
Small |
Small |
H5 |
Residents
in Ha Hang |
Medium,
there are both natural and built forms visible |
Irreversible |
500 |
Medium |
Low |
Temporary |
Permanent |
Small |
Small |
H6 |
Residents
in Casa Marina, Forest Hill, Richwood Park, Typhoon Place |
High,
these areas are larger scale developments with other development visible |
Irreversible |
1200 |
Medium |
Low |
Temporary |
Permanent |
Negligible |
Negligible |
H7 |
Residents
in A Sha, Tsin Lam, A |
Medium,
there are both natural and built forms visible |
Irreversible |
1500 |
Medium |
Low |
Temporary |
Permanent |
Negligible |
Negligible |
O1 |
Workers
at Tai Po Industrial Estate |
High,
these areas are more intensely developed |
Irreversible |
50 - 500 |
Small |
Low |
Temporary |
Permanent |
Negligible |
Negligible |
O2 |
Workers
at Hong Kong Institute of Education |
High,
these areas are more intensely developed |
Irreversible |
1000 |
Small |
Low |
Temporary |
Permanent |
Negligible |
Negligible |
T1 |
Travellers
along Ting Kok Road |
High, Sha
Lo Tung road upgrade is compatible with existing road |
Irreversible |
30 |
Small |
Low |
Temporary |
Permanent |
Small |
Small |
T2 |
Travellers
along Fung Yuen Road |
Medium,
there are both natural and built forms visible |
Irreversible |
200 |
Small |
Low |
Temporary |
Permanent |
Small |
Small |
T3 |
Travellers
along Sha Lo Tung Rd |
Medium,
the existing road is being upgraded |
Irreversible |
5 |
Large |
Medium |
Temporary |
Permanent |
Large |
Large |
The degree
of visual impact or significance threshold was rated in a similar fashion to
the landscape impact, ie significant, moderate,
slight and negligible. Where the matrix
table indicates a range within the significance threshold, eg;
Moderate – Significant, the final
significance threshold is assigned based on the overall severity of the impact.
The
visual impact is a product of the magnitude of change to the existing baseline
conditions, the landscape context and the sensitivities of VSRs
(refer Table 10.1). The significance threshold of visual impact
was rated for the construction phase and for Day 1 and Year 10 of the operation
phase.
10.10.14
Visual Mitigation Measures
The proposed landscape and visual mitigation measures
for impacts caused during the construction and operation phases are described
in Table 10.2, together with the
associated funding, implementation, management and maintenance agencies, and
the proposed implementation programme.
The mitigation measures are shown on plan in Figures 10.5a - 10.5d inclusive. The locations of viewpoints selected for
photomontage is shown in Figure 10.14 and various
views experienced by VSRs are illustrated in Figures 10.18 – 10.29.
10.10.15
Existing VSRs
All of the VSRs within the
visual envelope are mapped in Figure 10.13.
10.10.16
Prediction of Significance of Visual
Impacts
An assessment of the potential significance of the
visual impacts during the construction and operation phases, before and after
mitigation, is listed in detail in Table
10.8. Residual impacts are described
below. This follows the methodology
outlined above and assumes that the appropriate mitigation measures identified
in Tables 10.2 would be implemented,
and that the full effect of the soft landscape mitigation measures would be
realised after ten years. Photomontages
of the proposed development before and after mitigation are illustrated in Figures 10.18-10.29.
Construction Phase
Residual visual impacts in the Construction Phase are
mapped in Figure 10.15
VSRs
North of Project areas R4, R5, R8 and R9
·
Due
to the undulating topography and existing vegetation within the Sha Lo Tung
Valley, short distance views towards the Development Site will be limited. Visitors to Cheung Uk (R4) and Lei Uk (R5)
abandoned villages may have glimpses of the Development Site on the walking
trails across Sha Lo Tung Valley. They
will have closer views of the construction of the temporary footbridge and
fencing at Lei Uk village, however, the works in
these areas will be relatively small in scale.
The presence of construction equipment on the Development Site will
contrast with the existing natural surroundings,
however mitigation measures such as early planting works and colourings of site
hoardings will help to reduce these impacts to ‘Moderate’.
·
Hikers
on the Wilson Trail to the north of the site (R8) and on trails within the Pat
Sin Leng Country Park (R9), will have some long distance
views (>2000m) of the Development Site.
The presence of construction equipment on the Development Site will
contrast adversely with the existing natural surroundings, however, given the
long distance involved and the few numbers of VSRs,
the un-mitigated impact significance is considered ‘Moderate’ during
construction for these VSRs. The adoption of construction mitigation
measures particularly those involving soft landscape elements will help reduce
the residual construction impact but it will remain ‘Moderate’ for Hikers in
the Pat Sin Leng Country Park (R9).
VSRs
East of Project areas R10, O2, H5, H6 and H7
·
There
are very few VSRs located to the east of the site.
Whilst a number of walking trails are shown on some hiking maps, a number of site
visits to these areas could not locate these trails. As shown in Figure 10.26, a number of walking trails are indicated on
the Countryside Series maps. Site
inspection revealed that these paths are largely overgrown and could not be
accessed. Should access to these trails
become available, the sections do indicate that parts of the development may be
visible, however any VSRs who can access these trails
(shown as R 10), is only likely to experience ‘Slight’ residual construction
based impacts, due to the very few numbers of VSRs,
and the long viewing distance, and the dense vegetation in this area.
·
Residents
at Ha Hang (H5) may experience long distance glimpses of the road improvement
works from elevated vantage points.
These will be reduced by the proposed mitigation measures resulting in
‘Slight’ residual construction impacts.
·
The
GIS analysis also shows that some residential areas east of the site (H6 &
H7) and occupational VSRs (O2) may be able to see
some construction activities associated with the Sha Lo Tung Road improvement
works. This analysis does not take into
account the screening effect of the extensive existing vegetation. Views of the
construction works are likely to be only glimpses from elevated view points
within these areas. The residual impact
significance is therefore considered ‘Negligible’.
VSRs
South of Project areas R2, O1, T1 and T3
·
Users
of the Sha Lo Tung Road (T3) will come into close proximity to the road
improvement works at various locations along the road. New cut slopes, slope
upgrades, soil nailing and some tree removal will be required. The un-mitigated construction impact is
considered to be ‘Substantial’. With the
adoption of the mitigation measures proposed, these impacts will reduce to
‘Moderate’ during construction.
·
Cyclists
along Ting Kok road (R2). These VSRs
may experience a glimpse of the Sha Lo Tung Road improvement works as the VSR
passes the construction site and are likely to last a matter of seconds. The construction mitigation measures such as
site hoardings will reduce the visual impacts, with residual construction
impacts identified as ‘Moderate’.
·
Travellers
along Ting Kok Road (T1) may experience glimpses of
the road improvement construction works.
These will be short and intermittent as the VSRs
move along these roads. The residual
construction impacts are considered ‘Slight’.
·
Impacts
to workers at Tai Po Industrial Estate (O1) will be ‘Negligible’ as the project
works not visible from this area. The
works will be visible from Ting Kok Road, however these impacts are explained in T1 VSRs.
VSRs
West of Project areas R1, R3, R6, R7, H1, H2, H3, H4 and T2
·
Hikers
on the Wilson Trail (R1) and hikers within the Pat Sin Leng
Country Park (R3) to the east of the site will have clear views across the
whole Development Site and the presence of construction equipment will contrast
with the natural surroundings. The new
development will be the first close range development within the surrounding
areas, and thus during construction will present a ‘Substantial’ un-mitigated
visual impact for R1 and R3 during the construction phase. Following the implementation of the
mitigation measures the impacts to these groups of VSRs
will reduce to ‘Moderate’.
·
Hikers
on the path between Fung Yuen Valley up to Sha Lo Tung road
(R6) will experience views of various parts of the road improvement
works, which will change as the VSR moves towards or away from Sha Lo Tung
Road. The construction works associated
with the road improvement will contrast negatively with the surrounding natural
landscape however the adoption of the proposed construction mitigation measures
such as site hoardings will effectively reduce these impacts. The residual construction impacts will be
‘Moderate’.
·
Hikers
in the Fung Yuen valley (R7) are very few in number,
but may experience long distance views across the valley looking towards the
east of the road improvement works.
Glimpses of the construction activities will be available, and will
contrast with the natural appearance of the hillside. The mitigation measures proposed will help to
reduce these impacts. The residual
construction impacts will be ‘Moderate’.
·
The
residents of Fu Heng Estate (H1), residents of Pine
Hill, Yue Kok Tsuen and Tit Mei Tsai (H2) may experience long distance
glimpses of the road improvement works from elevated vantage points. These will be reduced by the proposed
mitigation measures. The residual construction impacts will be ‘Slight’.
·
Residents
of Fung Yuen village (H3) will experience views of the road construction works
and these works will contrast negatively with the surrounding natural
landscape. The mitigation measures such
as site hoardings will help to reduce these impacts. Early planting works will also help in
shortening the time frame for the visible construction works. The residual construction impacts will be
‘Slight’.
·
Residents
of the proposed new Fung Yuen Development (H4) are likely to see the
construction works associated with the road improvement and these works will
contrast negatively with the surrounding natural landscape. In addition, residents of the upper floors
(likely to be approximately 22 storey high) may also
have glimpses on construction equipment associated with the site formation
works at the Development Site. The
proposed mitigation measures such as site hoardings and early planting works
will help to reduce these impacts. The
residual construction impacts will be ‘Slight’.
·
Travellers
along Fung Yuen Road (T2) will experience glimpses of the Sha Lo Tung Road
improvement works. This will result in
‘Slight’ residual construction impacts.
Operation Phase
Residual visual impacts in the Operation Phase for
Day 1 and Year 10 are mapped in Figure 10.16 and 10.17 respectively. The
designs of the buildings within the Development Site have undergone a rigorous design
process to integrate the structures in to the surrounding landscape. In addition there is a high level of
landscape associated with the development that will not only reduce the visual
impacts but add to the amenity of the development. Following the adoption of the mitigation
measures proposed, the residual visual impacts during
operation will be as follows:
VSRs
North of Project areas R4, R5, R8 and R9
·
Hikers
on the Wilson Trail to the north of the site (R8) and on trails within the Pat
Sin Leng Country Park (R9), will have some long
distance views (>2000m) of the Development Site. The sensitive architectural design in
conjunction with the extensive landscape design will result in ‘Slight’ visual
impacts during Day 1 of operation. As
the vegetation matures, these will reduce to ‘Negligible’ at year 10.
·
Visitors
to Chueng Uk
and Lei Villages (R4 and R5 respectively) will experience ‘Moderate’ residual
visual impacts at Day 1 of operation.
These VSRs will be able to see permanent fence
as well as the Development Site. As the
vegetation and landscape matures around the development and adjacent to the
fence and the temporary footbridge is removed, these impacts will reduce to
‘Slight’ at Year 10 of operation.
VSRs
East of Project areas R10, O2, H5, H6 and H7
·
The
hikers in Pat Sing Leng Country Park to the east of
the site (R10) will experience long distance glimpses of the Development
Site. With the adoption of all the
mitigation measures, the visual impact significance will be ‘Slight’ at Day 1 of
operation reducing to ‘Negligible’ at Year 10 of operation as the vegetation
matures at Year 10.
·
All
other VSRs east of the project areas will experience
‘Negligible’ residual visual impacts during operation as the development is not
visible.
VSRs
South of Project areas R2, O1, T1 and T3
·
Travellers
along Sha Lo Tung Road (T3) will come into close proximity to the road
improvement works and will also come into close proximity of the Nature
Interpretation Centre and will therefore experience a ‘Substantial’ un-mitigated
visual impact. Following the adoption of
all proposed mitigation measures, this will reduce to a
‘Moderate’ visual impacts at Day 1 of operation. As the vegetation and green slopes mature,
these will reduce to ‘Slight’ during year 10 of operation.
·
Cyclists
along Ting Kok Road (R2) will experience ‘Moderate’
visual impacts at Day 1 of Operation, however as the vegetation matures along
the new cut-slopes this will reduce to ‘Slight’ at Year 10 of operation.
·
Workers
within Tai Po Industrial Estate (O1) will not have any views of the development
and therefore will experience a ‘negligible’ visual impact. Similarly travellers along Ting Kok Road (T1) may experience glimpses of the realigned
entry to Sha Lo Tung Road, however due to the very short viewing time and the
complementary nature of the road improvement works to Ting Kok
road, this is considered a ‘Negligible’ impact.
VSRs
West of Project areas R1, R3, R6, R7, H1, H2, H3, H4 and T2
·
Hikers
on the Wilson Trail to the west of the site (R1) will experience elevated views
of the Development Site and sections of the improved Sha Lo Tung Road. The visual impacts before the adoption of
mitigation measures are considered to be ‘Substantial’. However following the adoption of the
mitigation measures including the sensitively designed structures, high level
of landscaping and the adoption of the mitigation measures, the visual impacts
will reduce to ‘Moderate’ for these VSRs at Day 1 and
further reducing to ‘Slight’ at Year 10 of operation.
·
Hikers
within the Pat Sin Leng Country Park to the west of
the site (R3) will have un-obstructed views of the Development Site and
sections of the improved Sha Lo Tung Road.
They may also come into close proximity of the Nature Interpretation
Centre. The visual impacts before the adoption of mitigation measures are
considered to be ‘Substantial’. However
following the adoption of the mitigation measures including the sensitively
designed structures, high level of landscaping and the adoption of the
mitigation measures, the visual impacts will reduce to ‘Moderate’ for these VSRs at Day 1 and further reducing to ‘Slight’ at Year 10
of operation.
·
Hikers
on the path from Fung Yuen valley to Sha Lo Tung Road (R6) and Hikers within
Fung Yuen Valley (R7) will have views of the Sha Lo Tung Road improvement works
resulting in ‘Moderate’ impacts at Day 1 of operation. As the vegetation and cut slope plantings
mature, this will reduce to ‘Slight’ at Year 10 of operation.
·
For
Residents of Fu Heng Estate (H1), Residents in Pinehill, Yue Kok
Tsuen, Tit Mei Tsai (H2), Residents at Fung Yuen
Village (H3) and Residents of new Fung Yuen development (H4), only small
glimpses of the development may occur.
Following the adoption of the proposed mitigation measures the expected
visual impacts will be ‘Negligible’.
·
Similarly
for users of Fung Yuen road (T2), the adoption of the proposed mitigation
measures will result in a ‘Negligible’ visual impact.
Table
10.8 Significance of Visual Impacts in the Construction, Operation /
Restoration and Aftercare Phases (Note: All impacts adverse unless otherwise
noted)
VSR
Type & ID. |
Key
Visually Sensitive Receiver (VSR) |
Location
relative to project |
Degree
of Visibility of Source(s) of Visual Impact
(Full, Partial, Glimpse) & Distance Between VSR & Nearest
Source(s) of Impact |
Magnitude
of Change BEFORE Mitigation (Negligible,
Small, Intermediate, Large) |
Receptor
Sensitivity & Number
|
Impact
Significance BEFORE Mitigation (Negligible,
Slight, Moderate, Substantial) |
Recommended
Mitigation Measures |
Residual
Impact Significance Threshold AFTER Mitigation (Negligible,
Slight, Moderate, Substantial) |
|||||
Construction |
Operation |
||||||||||||
|
Operation |
Construction |
Operation |
Sensitivity (Low, Medium, High) |
Number (Very Few, Few, Many, Very Many) |
Construction |
Operation |
|
(Substantial, Moderate, Slight Negligible) |
DAY 1 |
YEAR 10 |
||
R1 |
Hikers on the Wilson trail
west of project areas |
West |
Full, 1000 |
Intermediate |
Intermediate |
High |
Few |
Substantial |
Substantial |
All |
Moderate |
Moderate |
Slight |
R2 |
Cyclists along Ting Kok Road |
South |
Glimpse, 10-50 |
intermediate |
Intermediate |
Medium |
Few |
Moderate |
Moderate |
CM12 |
Moderate |
Moderate |
Slight |
R3 |
Hikers within the Pat Sing Leng Country Park west of site |
West |
Glimpse, 500 - 2300 |
Large |
Large |
High |
Very Few |
Substantial |
Substantial |
All |
Moderate |
Moderate |
Slight |
R4 |
Visitors to Chueng Uk Village |
North |
Development, - glimpse, 200 Fence – full, 50 |
Intermediate |
Intermediate |
Medium |
Very Few |
Moderate |
Moderate |
DM1, 2, CM1, 2, 3, 6, 8, 12 |
Moderate |
Moderate |
Slight |
R5 |
Visitors to Lei Uk Village |
North |
Development, - glimpse, 200 Fence – full, 10 |
Intermediate |
Intermediate |
Medium |
Very Few |
Moderate |
Moderate |
DM1, 2, CM1, 2, 3, 6, 8, 12 |
Moderate |
Moderate |
Slight |
R6 |
Hikers on path from Fung
Yuen to Sha Lo Tung Road |
West |
Partial 10-200 |
Intermediate |
Intermediate |
Medium |
Few |
Moderate |
Moderate |
CM2, 3, 10, 11, 12 |
Moderate |
Moderate |
Slight |
R7 |
Hikers walk in Fung Yuen
Valley |
West |
Partial 500-1000 |
Intermediate |
Intermediate |
Medium |
Very Few |
Moderate |
Moderate |
CM2, 3, 10, 11, 12 |
Moderate |
Moderate |
Slight |
R8 |
Hikers on Wilson Trail
north of project areas |
North |
Partial 1500 |
Small |
Small |
High |
Few |
Moderate |
Moderate |
All |
Moderate |
Slight |
Negligible |
R9 |
Hikers in Pat Sin Leng Country Park North of project areas |
North |
Glimpse 700 |
Small |
Small |
High |
Very Few |
Moderate |
Moderate |
DM1, 2, 3, CM1, 2, 3, 6, 8,
12 |
Moderate |
Slight |
Negligible |
R10 |
Hikers in Pat Sin Leng Country Park East of project areas |
East |
Glimpse 700 - 2000 |
Small |
Small |
High |
Very Few |
Moderate |
Moderate |
DM1, 2, 3, CM1, 2, 3, 6, 8,
12 |
Slight |
Slight |
Negligible |
H1 |
Residents of Fu Heng Estate |
West |
Glimpse 2000 |
Small |
Small |
High |
Many |
Moderate |
Moderate |
DM1, 2, CM1, 2, 3, 6, 8, 12 |
Slight |
Negligible |
Negligible |
H2 |
Residents in Pinehill, Yue Kok Tsuen, Tit Mei Tsai |
West |
Glimpse 200 - 1000 |
Small |
Small |
High |
Many |
Slight |
Slight |
DM1, 2, CM1, 2, 3, 6, 8, 12 |
Slight |
Negligible |
Negligible |
H3 |
Residents at Fung Yuen
Village |
West |
Partial 300 |
Small |
Small |
High |
Many |
Moderate |
Moderate |
DM1, 2, CM1, 2, 3, 6, 8, 12 |
Slight |
Negligible |
Negligible |
H4 |
Residents of new Fung Yuen
development |
West |
Partial 300 |
Small |
Small |
High |
Many |
Moderate |
Moderate |
DM1, 2, CM1, 2, 3, 6, 8, 12 |
Slight |
Negligible |
Negligible |
H5 |
Residents in Ha Hang |
East |
Glimpse 500 |
Small |
Small |
High |
Many |
Slight |
Slight |
DM1, 2, CM1, 2, 3, 6, 8, 12 |
Slight |
Negligible |
Negligible |
H6 |
Residents in Casa Marina,
Forest Hill, Richwood Park, Typhoon Place |
East |
Glimpse 1200 |
Negligible |
Negligible |
High |
Many |
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
Negligible |
H7 |
Residents in A Sha, Tsin Lam, A |
East |
Glimpse 1500 |
Negligible |
Negligible |
High |
Few |
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
Negligible |
O1 |
Workers at Tai Po
Industrial Estate |
South |
Glimpse 50 - 500 |
Negligible |
Negligible |
Low |
Many |
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
Negligible |
O2 |
Workers at Hong Kong
Institute of Education |
East |
Glimpse 1000 |
Negligible |
Negligible |
Low |
Few |
Negligible |
Negligible |
Nil |
Negligible |
Negligible |
Negligible |
T1 |
Travellers along Ting Kok Road |
South |
Glimpse 30 |
Small |
Small |
Low |
Many |
Slight |
Slight |
CM13 |
Slight |
Negligible |
Negligible |
T2 |
Travellers along Fung Yuen
Road |
West |
Glimpse 200 |
Small |
Small |
Low |
Few |
Slight |
Slight |
DM1, 2, CM1, 2, 3, 6, 8, 12 |
Slight |
Negligible |
Negligible |
T3 |
Travellers along Sha Lo
Tung Rd |
South |
Full 5 |
Large |
Large |
Medium |
Few |
Substantial |
Substantial |
DM1, 2, CM1, 2, 3, 6, 8, 12 |
Moderate |
Moderate |
Slight |
* O = Occupational; H = Residential; R =
Recreational; T = Travelling. |
10.11
Environmental
Monitoring and Audit
It is recommended that EM&A for landscape and
visual resources is undertaken during the design, construction and operation
stages of the Project. The design,
implementation and maintenance of landscape mitigation measures is a key aspect
of the project and should be checked to ensure that they are fully realised and that potential conflicts between the proposed
landscape measures and any operational requirements are resolved at the
earliest possible date and without compromise to the intention of the
mitigation measures. In addition,
implementation of the mitigation measures recommended by the EIA will be
monitored through the site audit programme throughout
construction and operation phases.
Fourteen Landscape Resources and four Landscape
Character Areas were identified within the 500 metre Study Area.
A number of mitigation measures have also been
proposed for both the design and construction period to not only reduce
potential landscape and visual impacts but also to improve the overall amenity
of the Project.
The following residual landscape impacts have been
identified during the construction phase:
·
There will be ‘Moderate’ impacts on LR1 Woodland, LR2 Open Shrubland, LR6 Plantation, LCA1 Upland and Hillside
Landscape and LCA4 Sha Lo Tung Valley.
·
There will be ‘Slight’ impacts on LR3 Abandoned Agricultural Land, LR4
Developed Area, LR7 Roads and LCA2 Fung Yuen Valley.
·
There will be ‘Negligible’ residual impacts of all other LRs and LCAs during the
construction phase.
The following residual landscape impacts have been
identified during the operation phase:
·
During the operation phase, there will be ‘Moderate’ residual landscape
impacts on LCA4 Sha Lo Tung Valley at Day 1 of operation, reducing to ‘Slight’
at Year 10 of operation.
·
There will be ‘Slight’ impacts on LR1 Woodland, LR2 Open Shrubland, LR2 Open Shrubland,
LR6 Plantation and LCA1 Upland and Hillside Landscape at Day 1 of operation. At
year 10 of operation, ‘Slight’ impacts will remain for LR1 Woodland, LR 3
Abandoned Agricultural Land and LCA1 Upland and Hillside Landscape. The impacts will reduce to ‘Negligible’ for
LR3 Abandoned Agricultural Land and LR6 Plantation.
·
There will be ‘Negligible’ residual impacts of all other LRs and LCAs during the operation
phase at both Day 1 and Year 10.
In
addition to a review of the physical barriers forming the natural visual
envelope of the project, a GIS analysis and an analysis of the parameters of
human vision was undertaken. The visual
envelope was found to extend to 2.3km from the boundary of the Development Site
and 900m from the road improvement works.
Ten
recreational, seven residential, two occupational and three travelling VSRs were identified within the visual envelope.
The following residual visual impacts have been
identified during the construction phase:
·
Temporary residual visual impacts of ‘Moderate’ significance will
include R1 Hikers on the Wilson Trail west of the site, R2 Cyclists along Ting Kok Road, R3 Hikers within the Pat Sin Leng
Country Park west of the site, R4 and R5 visitors to Cheung Uk
and Lei Villages, R6 Hikers on the path from Fung Yuen to Sha Lo Tung Road, R7
Hikers in Fung Yuen valley, R8 Hikers on the Wilson Trail north of the site, R9
Hikers in Pat Sin Leng Country Park North of project
areas and T3 Travelers along Sha Lo Tung Road.
·
Residual visual impacts of ‘Slight’ significance will include R10 Hikers
in Pat Sin Leng Country Park east of project areas.
Residential VSRs including H1 residents and Fu Heng Estate, H2 Residents in Pinehill,
Yue Kok Tsuen
and Tit Mei Tsai, H3 and H4 Residents in Fung Yuen village and the proposed new
Fung Yuen development and H5 Residents at Ha Hang will experience ‘Slight’
visual impacts. T1 and T2 Travelers
along Ting Kok and Fung Yuen roads will also
experience ‘Slight’ residual impacts.
·
All other VSRs will experience ‘Negligible’
impacts during construction.
The following residual visual impacts have been
identified during at Day 1 of the operation phase:
·
At Day 1 of the operation phase, ‘Moderate’ residual visual impacts have
been identified for R1 Hikers on the Wilson Trail west of the site, R2 Cyclists
along Ting Kok Road, R3 Hikers within the Pat Sin Leng Country Park west of the site, R4 and R5 visitors to
Cheung Uk and Lei Villages, R6 Hikers on the path
from Fung Yuen to Sha Lo Tung Road, R7 Hikers in Fung Yuen valley and T3
Travelers along Sha Lo Tung Road.
·
Residual visual impacts of ‘Slight’ significance at Day 1 of operation
will include R8 Hikers on the Wilson Trail north of the site and R9 and R10
Hikers in Pat Sin Leng Country Park north and east of
project areas.
·
All other VSRs will experience ‘Negligible’
residual visual impacts at Day 1 of operation.
·
At Year 10 of operation, ‘Slight’ impacts will remain for R1 Hikers on
the Wilson Trail west of the site, R2 Cyclists along Ting Kok
Road, R3 Hikers within the Pat Sin Leng Country Park
west of the site, R4 and R5 visitors to Cheung Uk and
Lei Villages, R6 Hikers on the path from Fung Yuen to Sha Lo Tung Road, R7
Hikers in Fung Yuen valley and T3 travelers along Sha Lo Tung road.
In accordance with Annex 10 of the EIAO-TM,
the landscape and visual impacts are considered acceptable with mitigation measures.