This section reports on the Study to assess the potential landscape and visual impacts arising from construction and operation of any above ground structures and works areas associated with the Schedule 2 DP 5 only. Please refer to Table 12.16.2 for details of how each package has been divided.
The components of DP Package B are summarised in Table 12B.1.1 below.
Table 12B.1.1 - Schedule
2 DP Package B
DP Package B |
|||
5 |
New Sewage Pumping Stations (SPS) in KTN NDA |
F3 |
A sewage pumping station---(b) with an installed
capacity of more than 2000 m3 per day
and a boundary of which is less than 150 m from an existing or planned
residential area or educational institution. 2no. SPS are proposed in KTN, these are: SPS south of Ma Tso Lung. SPS south of Ho Sheung Heung. |
This section provides an overview of the HKSAR Government’s development intentions, statutory land-use and planning within the Study Areas, specifically from landscape and visual standpoints. It considers relevant, published studies, such as HK2030 Study, OZPs, and DPA mapping. This information has been considered in relation to the relevant revised RODP of the NDAs and their Layout Plans with the aim of assessing whether the DP can fit into the surrounding setting.
12B.2.1
Design
measures adopted within the Schedule 2 Designated Projects
The Schedule 2 DPs form the key infrastructure developments to support the future development and population growth within the KTN and FLN NDAs. KTN and FLN NDAs will provide a mix of housing types as well as basic infrastructure and community facilities. The development opportunities and constraints of the Schedule 2 DPs are presented in Section 2.4.1, these have informed the development and consideration of alternative infrastructure options. A summary of the key design rationale for each project is provided below:
DP 5 - New sewage pumping stations (SPS) in KTN NDA
Two SPS are proposed in KTN NDA to convey the sewage flows from KTN NDA to Shek Wu Hui Sewage Treatment Works for treatment and its disposal, details on their operational requirements are presented in Section 2.4.2.5. The SPS south of Ma Tso Lung has been positioned to serve development proposals in this area. A site close to proposed road access and other built development has been selected so that built form is integrated together. The internal layout and configuration of the structure has been rationalised to minimise land take. Generally these buildings follow a standard format, that is, an external solid perimeter wall (approx. 3m high), internal access road with turning head and 5m high pumping station building enclosing the pumping plant. The buildings are rectangular single storey with a flat roof.
A second SPS south of Ho Sheung Heung is positioned close to the Sheung Yue River. The layout and footprint has been set back from the river frontage to reduce the visibility and retain the connectivity of riverside access paths. The internal layout and configuration of the structure has been rationalised to minimise land take. The structure is also located, where operationally feasible, close to or integrated within the proposed NDA development to avoid visual clutter.
Existing Outline Zoning Plans (OZPs)
The review of the OZPs has included a review of the Plans
as well as the accompanying Notes and Explanatory Statements. The DP sites and study areas have been
superimposed onto existing OZPs and DPA Plans to determine the potential
influence on the existing zoning. The
study area and site boundaries for the DP 5 sites are presented on Figure
12.50.2.
The KTN DP 5 study areas are covered by the following OZP/DPA documents:
·
Approved
Kwu Tung North OZP No. S/NE-KTN/8.
·
Draft
Kwu Tung South OZP No. S/NE-KTS/13
·
Approved
Ma Tso Lung and Hoo Hok Wai Development Permission Area Plan No. DPA/NE-MTL/2.
Table 12B.2.1 summarises the areas of existing zoning types which will be directly affected by the site boundary of each DP.
Table 12B.2.1 Schedule 2 Designated Project 5
Zoning Type |
OZP/DPA
number and extent of zoning within the site boundary that will undergo
change (ha) |
Comments on
Major land use changes |
DP5 – New Sewage Pumping
Stations |
||
Agriculture (AGR) |
S/NE-KTN/8 0.266 DPA/NE-MTL/2 0.277 |
Approximately 0.266ha of this zoning type will be modified to construct the KTN southern SPS located to the south of Ho Sheung
Heung. Approximately 0.277ha will be modified to
form the northern SPS south of Ma Tso Lung. |
Summary of land use changes
In the case of both SPS, these are located on land currently zoned as Agriculture which would be lost as a result of their construction, this amounts to approximately 0.543ha.
The methodology for Landscape Impact Assessment is presented in Section 12.18.
According to the Study Brief (ESB-176/2008) baseline review comprises the identification of all existing Landscape Resources (LR) and Landscape Character Areas (LCA) within 500m of the DP boundary.
The overall Study Area for all the DP is generally natural and rural. Complex LRs can be classified into different major categories, as follows:
· LR1 – Channelised Water Course
· LR2 – Water Course
· LR3 – Water Pond
· LR4 – Marsh/ Wetland
· LR5 - Plantation
· LR6 – Hillside Woodland
· LR7 – Lowland Woodland
· LR8 – Shrubland / Grassland Mosaic
· LR9 – Agricultural Land
· LR12 – Rural Development Area
· LR13 – Industrial / Open Storage
· LR14 – Major Transportation Corridor
The LCAs are classified as follows:
· LCA1 Natural Hillside Landscape
· LCA2 Rural and Urban Peripheral Village Landscape
· LCA4 Industrial Landscape
· LCA5 Lowland Agricultural Landscape
· LCA6 Major Transportation Corridor Landscape
· LCA7 Major Water Course Corridor Landscape
The landscape resources and landscape character areas of each NDA are described in further detail below, together with their sensitivity.
12B.3.1 Broad Brush Tree Survey
A broad brush tree survey has been carried out within the study area which estimates that around 10 trees will be affected by the proposed development. Major tree species included within the wider study area in include Acacia confusa, Acacia auriculiformis, Araucaria heterophylla, Bauhinia blakeana, Bombax ceiba, Cassia siamea, Celtis sinensis, Cinnamomum camphora, Clausena lansium, Citrus maxima, Dimocarpus longan, Eucalyptus camaldulensis, Ficus virens, Ficus microcarpa, Litchi chinensis, Leucaena leucocephala, Macaranga tanarius, Mangifera indica, and Melaleuca quinquenervia. Many trees are found in the foothills of the natural upland, as well as the rural fringe in between different villages and they are generally mature.
A detailed Tree Felling Application process will be carried out at a later detailed design stage, to finalise tree treatment and allocate compensatory planting areas including available open space, parks and streetscape.
A single (OVTs) is found within the Study Area of the SPS south of Ho Sheung Heung (ref. No. LCSD/ N45), its location is illustrated on Figure 12.51.12.
12B.3.2 Schedule 2 DPs 5 Baseline Landscape Resources (LRs) and Landscape Character Areas
The baseline LRs and LCAs of KTN DP 5 are detailed along with their sensitivity in Table 12B.3.1 and 12B.3.2; figures presenting this information are set out below:
Figure 12.51.2 LRs for DP 5.
Figure 12.51.11 and 12 LRs for DP 5 enlarged versions.
Figure
12.51.42 to 46 Representative images of LRs for DP 5.
Figure 12.52.2 LCAs for DP 5.
Figure
12.52.7 to 8 Representative
images of LCAs for DP5.
Table 12B.3.1 - Landscape Resources and their
Sensitivity- KTN NDA (DP5)
Id. No. |
Landscape Resource
(LR) |
Quality &
Maturity (High /Medium /Low) |
Rarity (High
/Medium /Low) |
Ability to
Accommodate Change |
Sensitivity |
KLR 1 – Channelised
Water Course |
|||||
Within the Study Area this LR includes a section of Sheung Yue River. This LR is a prominent feature within the landscape. |
|||||
1.3 |
Sheung Yue River |
Medium |
Medium |
Medium |
Medium |
Shek Sheung River collects water from the south and flows north,
joining Sheung Yue River west of Sheung Shui Slaughter House. There is also a branch that splits from Ng Tung
River and flows round the Shek Wu Hui Sewage Treatment Works to the south but
this is mainly dry and a flood protection measure. This LR is mainly a grasscrete lined,
trapezoidal channel, formed for the purpose of flood protection in Kwu Tung
and Fanling areas. Water partially
dries out during the dry season and there are small water channels at the
base of the channel when water flow is low, with grass on either side. |
|||||
This river is reasonably capable of accommodating change and its
sensitivity is considered to be medium. |
|||||
1.4 |
Water Course
Network in Long Valley |
Medium |
Low |
High |
Medium |
This LR sits outside the works area and will not be affected. This LR describes a
network of waterways in the Long Valley area which eventually connect and
flow into a box culvert near the Kwu Tung Road junction with Castle Peak
Road. The watercourses are mainly
vertically-sided concrete channels constructed for irrigation purposes with
limited vegetation. The riparian
vegetation that does exist comprises common and widespread herb species. This LR has a reasonable ability to accommodate change, being a
man-made network of water channels, but overall it is vital to the Long
Valley agricultural area for irrigation and its sensitivity is considered to
be medium. |
|||||
KLR 2 – Water
Course |
|||||
Refers to natural or semi-natural water courses, including short
sections with concreted banks. This LR
also includes vegetation associated with the water course, both within the
streams and along the banks as well as in the immediate vicinity. The vegetation mainly consists of grasses
and shrubs, but also includes trees in some areas such as the upland streams,
as detailed further in the individual LR descriptions. The vegetation often provides a subtle
transition between this LR and its surrounding LR(s). |
|||||
Within the Study Area this LR
includes watercourses running between different rural areas and villages,
incorporating streams running off Ma Tso Lung and around Kwu Tung
itself. |
|||||
2.1 |
Natural Streams in
Kwu Tung |
Medium |
Medium |
Medium |
Medium |
This LR sits outside the works area and will not be affected. These streams, connecting with the Sheung Yue River, are located
centrally within the Study Area. They
pass through villages including Fung Kong, Tung Fong, Tong Kok, Shek Tsai
Leng and south of Ho Sheung Heung. The
upstream section is natural but has been degraded by pollution, with seasonal
flows and heavily vegetated stream banks, overgrown with common grass species
such as Bidens alba and Pennisetum spp.
Other sections of these streams are fortified by concrete banks with
grey water flowing. |
|||||
This LR is relatively intolerant to change and its sensitivity is
considered to be Medium. |
|||||
2.4 |
Natural Streams at
Ma Tso Lung |
High |
Medium |
Low |
High |
This LR sits outside the works area and will not be affected. This LR describes natural streams running off Ma Tso Lung to the
lowland area in Ma Tso Lung San Tsuen in the northwest of KTN NDA Study Area.
Riparian plants included fruit trees (i.e. Dimocarpus longan and Litchi
chinensis) and native understory species (e.g. Lophatherm gracile and
Alocasia odora) and the vegetation near the streams is dominated by the
exotic climber species Mikania micrantha and herb species Bidens alba and
Alocasia macrorhizos. The section at Ma Tso Lung is regarded as ecologically
important due to its naturalness and well developed bank area. |
|||||
This LR is relatively intolerant to change and its sensitivity is
considered to be high. |
|||||
KLR 3 – Water Pond |
|||||
Refers to
freshwater ponds. The ponds are often associated
with agricultural land and used for irrigation, and punctuate the traditional
field pattern. Some ponds are also
found near residential or developed areas and have aesthetic, landscape value
and some are fish ponds. This LR also
includes vegetation associated with the ponds, both within and around the
banks as well as in the immediate vicinity.
The vegetation mainly consists of grasses and shrubs, with scarce
trees. |
|||||
The main locations
of these water ponds within the Study Area of KTN NDA (DP3 & 4) include both foothill and lowland areas and
are most concentrated in Ho Sheung Heung, Long Valley and the Closed
Area. |
|||||
3.1 |
Ho Sheung Heung
Water Ponds |
Medium |
Medium |
Low |
High |
This LR sits outside the works area and will not be affected. This LR is located within Ho Sheung Heung agricultural land and is a
relatively large continuous area of water ponds within the Study Area. These
ponds retain water most of the time including both the dry and wet
seasons. The bunds of these ponds are
vegetated by grasses and low shrubs, as well as some fruit trees such as Musa x paradisiaca, Litchi chinensis, Mangifera indica, Dimocarpus longan and Citrus maxima. |
|||||
The ponds in this area are of medium quality with common fruit trees
and are relatively intolerant to change.
The sensitivity of this LR is considered to be high. |
|||||
3.2 |
Long Valley Water
Pond |
Medium |
Medium |
Low |
High |
This LR sits outside the works area and will not be affected. This LR is located within Long Valley agricultural land. Water in the ponds is usually full in wet
season and periodically pumped out by local farmers for irrigation and
management purposes during dry season.
Grasses grow along their banks and provide a subtle transition between
this LR and its surrounding agricultural land. |
|||||
These ponds are relatively intolerant to change and their sensitivity
is considered to be high. |
|||||
3.8 |
Water Ponds within
the Closed Area |
Medium |
Medium |
Low |
High |
This LR sits outside the works area and will not be affected. Part of the Study Area lies within the Closed Area and the water ponds
of this LR within the Study Area are located just north of Ma Tso Lung. The ponds are small and generally overgrown
and abandoned, but are associated with agricultural land. |
|||||
This LR is relatively intolerant to change and its sensitivity is
considered to be high. |
|||||
KLR 4 – Marsh/
Wetland |
|||||
Refers to freshwater marsh/ wetland landscape resources, often found
at old river meanders which have been truncated during river channelization
and retraining, overgrown with herbaceous vegetation and often with some
areas of seasonal or permanent open water.
This LR also includes wetland areas along natural streams around Ma
Tso Lung as well as areas that were once ponds but have not been actively managed
for a long time. |
|||||
Within the Study Area, this LR is found in Long Valley, along the
channelized water courses as well as in the north around Ma Tso Lung. |
|||||
4.1 |
Marshes in Long
Valley |
Medium |
High |
Low |
High |
This LR sits outside the works area and will not be affected. This LR is generally located in the middle of Long Valley agricultural
land, including both permanent wet marshes and well vegetated marshes. For the permanent wet marshes, they used to
be fish ponds or irrigation ponds and have been
abandoned and inactively managed.
Densely emergent
vegetation is present in these marshes and shows relatively high diversity. Tree species include Phragmites
karka, sedges Cyperus iria and Kyllinga aromatica, and herbs and
climbers such as Ipomoea aquatica, Polygonum barbatum and Polygonum lapathifolium. For the well vegetated marshes, a large
portion of the wetland area is covered with rich and moist topsoil, colonised
by common and widespread species such as Brachiaria
mutica, Panicum maximum, Bidens alba, Ludwigia perennis and the Common Wetland Fern Cyclosorus interruptus. |
|||||
This LR is fairly rare and is relatively intolerant to change and its
sensitivity is considered to be high. |
|||||
4.2 |
Mitigation Wetland |
Medium |
High |
Low |
High |
This LR sits outside the works area and
will not be affected. Several plots of marsh are located along
the Sheung Yue River that borders the Long Valley agricultural land. They were formerly meanders of the river
and were isolated during the river channelisation. To mitigate the ecological impact resulting
from channelisation, these areas are now managed by a government department
to provide marsh habitat, mainly for wetland dependent wildlife. As part of the habitat management, wetland
plants and riparian vegetation have been planted. These plants include Commelina diffusa, Hedychium
coronarium, Ludwigia perennis and
Nelumbo nucifera. Bamboos and trees are also planted along
the bunds, e.g. Acacia auriculiformis,
Cinnamomum camphora, Hibiscus tiliaceus and Ilex rotunda. |
|||||
Mitigation habitats are fairly rare in Hong Kong and additionally,
this LR is relatively intolerant to change.
Its sensitivity is considered to be high. |
|||||
KLR-4.3 |
Wetland/ Marsh in
the Closed Area |
Medium |
Medium |
Low |
High |
This LR sits outside the works area and will not be affected. The area of this LR along the natural stream in northern Ma Tso Lung
appears to have evolved from agricultural land that has been abandoned for a
long time and is influenced by the water course, such that the land is mainly
wet underfoot. The wetland vegetation
is dominated by the exotic grass Brachiaria
mutica and creeper Ipomoea cairica as
well as native herbs including Commelina
diffusa, Colocasia esculenta, Cyclosorus interruptus,Ludwigia perennis and
Pennisetum purpureum. Riparian vegetation is dominated by the exotic
climber species Mikania micrantha
and herb species Bidens alba and Alocasia macrorhizos. Abandoned ponds north of Ma Tso Lung, likely
previously used as fish ponds or for irrigation purposes have been abandoned
for a long time and now have dense emergent vegetation present in them such
that they are considered marshes. They
include vegetation such as
exotic wetland species such as Brachiaria mutica and Sesbania
cannabina and the invasive exotic tree species Leucaena leucocephala but
also support some native wetland herb species including Polygonum
japonicum, Commelina diffusa and Ludwigia octovalvis. |
|||||
This LR is relatively intolerant to change due to the succession of
vegetation and the natural sensitivity of wetland/marsh. Its sensitivity is considered to be high. |
|||||
KLR 5 Plantation |
|||||
Refers to medium sized and larger clusters of trees that have been
planted and are distinct from natural woodland since they have been planted
by man. Common tree species in this LR
include native (Ficus microcarpa, Celtis sinensis, Cinnamomum camphora and Macaranga
tanarius) and exotic species (Acacia
confusa, Casuarina equisetifolia
and Melaleuca quinquenervia) and
further details are given in the individual LR descriptions. |
|||||
Within the Study Area of KTN NDA (DP 5) this LR includes a
single OVT, reference no. LCSD/ N45
located on Castle Peak Road, the trees species is Melaleuca quinquenervia. |
|||||
5.4 |
Old and Valuable
Trees (OVT) Castle Peak Road |
High |
High |
Low |
High |
This LR sits outside the works area and will not be affected. 5no. Old and Valuable Trees (OVTs) are located within KTN along Castle
Peak Road, a single OVT (reference number LCSD N/45) sits within the
study area of DP5. The tree species is
Melaleuca cajuputi subsp. Cumingiana, 18m
high with a crown spread of 13m. The
tree sits within the narrow verge between castle peak road and the Fanling
Highway surrounded by road surfacing. |
|||||
This LR has a low capacity to accommodate change and its sensitivity is
considered to be high. |
|||||
KLR 6 – Hillside
Woodland |
|||||
Refers to woodland areas largely scattered over hillsides, including
at the base of hills. This LR is
predominantly composed of native tree species and is generally located some
distance from human activities (and hence disturbance), growing naturally
with some understorey vegetation. It
can include areas of Fung Shui Woodland growing in hillsides in the vicinity
of village. Common tree species in
this LR include Macaranga tanarius,
Leucaena leucocephala, Celtis sinensis and Ficus microcarpa. Further
details are given in the individual LR descriptions. |
|||||
Within the Study Area of the KTN NDA (DP5), this LR is found
at the hillsides of Ma Tso Lung and northwest of Ho
Sheung Heung. |
|||||
6.3 |
Hillside Woodland
in Ma Tso Lung, Tit Hang and Fung Kong |
High |
Medium |
Low |
High |
This LR sits
outside the works area and will not be affected. This LR refers to the narrow, winding and largely
continuous patches of woodland in the hillside areas of Ma Tso Lung San
Tsuen. Woodlands in these areas predominantly border uphill
shrubland/grassland areas and lowland woodlands, and sometimes adjoin rural
and industrial areas. Due to limited
human disturbance, these trees are mature in medium to large sizes. Dominant tree species include both native
and exotic ones. Dominant native trees
are Ficus hispida, Cinnamomum camphora, Rhus succedanea, Celtis sinensis,
Ficus microcarpa and Macaranga tanarius.
Dominant exotic species include Melaleuca quinquenervia, Leucaena
leucocephala, Melia azedarach, Acacia confusa and Casuarina equisetifolia. |
|||||
This LR is considered to be relatively mature and of
high quality and it has little capacity to tolerate change. The sensitivity of this LR is considered to
be high. |
|||||
6.4 |
Ho Sheung Heung
Fung Shui Woodland |
High |
High |
Low |
High |
This LR sits outside the works area and will not be affected. Ho Sheung Heung Fung Shui Woodland is bound by Ho Sheung Heung Road,
Ho Sheung Heung Pai Fung Road and Chung Kuk Path and covers a small
hill. It used to be a complete area of
woodland with continuous canopy but has been fragmented by hill fires
recently. Grasses and shrubs have now colonised the bald areas to connect the
woodland patches. Apart from Aquilaria sinensis, a species of
conservation interest, other typical Fung Shui Woodland trees are also found,
such as Garcinia oblongifolia,
Sterculia lanceolata and Litsea
glutinosa. Other dominant trees include native species Celtis sinensis, Ficus microcarpa, Ficus
hispida, Macaranga tanarius, Bischofia javanica, Cinnamomum camphora, Microcos paniculata and Schefflera heptaphylla and exotic
species Acacia confusa, Bombax ceiba,
Dimocarpus longan and Melia
azedarach of medium to large sizes. |
|||||
This Fung Shui Woodland has high amenity and cultural value and is
intolerant to change. Its sensitivity
is considered to be high. |
|||||
KLR 7 – Lowland Woodland |
|||||
Refers to woodland growing on low lying ground (generally <40 mPD),
often found near rural village areas in small, fragmented patches, with
differing tree species according to location.
This LR can be found in patches within areas of human activity and
also includes some Fung Shui Woodland of particular cultural importance,
located adjacent to certain villages as detailed in the individual
descriptions. Common plant species in
this LR include Acacia confusa, Celtis
sinensis, Cinnamomum camphora, Leucaena leucocephala and Macaranga tanarius. Further details are given in the individual
LR descriptions. |
|||||
Within the Study Area of KTN NDA (DP5) this LR includes
woodland in Tong Kok |
|||||
7.3 |
Lowland Woodland in
Pak Shek Au and Tong Kok |
High |
Medium |
Low |
High |
This LR sits outside the works area and will not be affected. This LR refers to the lowland woodlands at Pak Shek Au and Tong Kok,
north of Fanling Highway. These
woodlands are largely surrounded by adjacent industrial/open storage areas
and therefore potentially suffer from disturbance by human activities. This LR also includes an old developed area
west of Dills Corner that has now become completely overgrown with woodland. |
|||||
The trees in this woodland are of medium to large
sizes, and are dominated by both native and exotic species. The most abundant
native species include Ficus microcarpa, Bischofia javanica, Cinnamomum camphora,
and Macaranga tanarius, while
exotic species include Acacia confusa,
Bombax ceiba, Dimocarpus longan, Delonix regia, Averrhoa carambola, Casuarina equisetifolia, Chukrasia tabularis,
Leucaena leucocephala and Spathodea
campanulata. This LR has a medium to high amenity value and a low capacity to
tolerate change and it sensitivity is considered to be high. |
|||||
KLR 8 – Shrubland /
Grassland Mosaic |
|||||
Refers to a mosaic of shrubland and grassland which is usually large
in size and uniform in appearance.
This LR is typical of the fire-maintained hill-slopes in Hong Kong and
common species include grasses such as Imperata koenigii, Neyraudia
reynaudiana, Bidens alba, Panicum maximum and Miscanthus spp., fern
Dicranopteris pedata and shrubs Baeckea frutescens, Breynia fruticosa, Litsea
rotundifolia var. oblongifolia and Rhaphiolepis indica. |
|||||
Within the Study Area of KTN NDA (DP5), this LR is found mainly on
hillsides, particularly on the upper areas of Fung Kong Shan, Ki Lun Shan,
Tai Shek Mo and its western foothill and forms a large part of the Study
Area. Further details are given in the individual LR descriptions. |
|||||
8.3 |
Shrubland/Grassland
Mosaic in Tai Shek Mo and the Western Range Foothills |
Medium |
Low |
Medium |
Medium |
This LR is an extensive area of shrubby grassland on the uplands of
Tai Shek Mo and the foothills of the Western Ranges covering Ma Tso
Lung. It largely merges into hillside
woodland in at the foothills and is sometimes adjacent to some rural and urban
development areas. Similar to the
other hilly shrubland/grassland in Hong Kong, this LR is also maintained by
periodical hill fires. |
|||||
This LR can re-establish itself fairly easily and is therefore
considered to be relatively tolerant to change. Its sensitivity is medium. |
|||||
KLR 9 - Agricultural Land |
|||||
Refers to land used for agriculture
including crops and orchards as well as ornamental plant nurseries. This LR contains a small number of
structures such as small irrigation ponds, green houses, equipment sheds and
small/ narrow hard paved areas. It not
only contains agricultural vegetation but also some scattered
non-agricultural vegetation including some shrubs and trees. It is often an intermediary between areas
of development and natural areas. |
|||||
Within the Study Area of the KTN NDA (DP5), this LR is mainly
found in Long Valley, Ho Sheung Heung, Shek Tsai Leng, Tong Kok and Tung
Fong. |
|||||
9.1 |
Long Valley
Agricultural Land |
High |
High |
Low |
High |
This LR sits outside the works area and will not be affected. This LR in Long Valley consists mainly of wet agriculture and includes
both active and inactive fields.
Common wetland crops in Long Valley include Ipomoea aquatica and Nasturtium
officinale, with some fields cultivated with Eleocharis dulcis, Oryza
sativa and Trapa bispinosa. Water lily (Nymphaea sp.) and Lotus (Nelumbo
nucifera) are also cultivated in some ponds with shallow water. Dry land crops include Aloe vera var. chinensis,
Allium tuberosum, Brassica chinensis, and Lactuca sativa. Fruit trees are present along field bunds
including Dimocarpus longan, Litchi chinensis and Magnifera indica. |
|||||
This LR in Long Valley is of good quality and high significance in
terms of crop production and being a large contiguous area of agriculture in
Hong Kong. Although agricultural land
per se is fairly easy to re-establish given the right environment, given the
size of this LR and lack of similar areas in Hong Kong, it is relatively
intolerant to change and its sensitivity is high. |
|||||
9.3 |
Agricultural Lands
in Shek Tsai Leng, Tong Kok and Fung Kong |
Low |
Low |
Medium |
Medium |
These agricultural lands scattered in the centre of the study area of
KTN and are associated with the villages in Shek Tsai Leng, Tong Kok and Fung
Kong, where they are surrounded by industrial or open storage areas. Most of the agricultural lands within this
area are abandoned with weeds and invasive trees (e.g. Leucaena leucocephala) beginning to colonize the land and turning
it to wasteland. In some locations,
common vegetable plants, such as Lactuca
sativa, are still found being cultivated in the small areas of farmland
that are still active. |
|||||
This LR is mostly abandoned and does not have high value in terms of
crop production but does provide some green space between the hard surfaces
of industrial/open storage areas or rural development areas. Agricultural land is fairly easy to
re-establish given the right environment, and is relatively tolerant to
change but given the greening element amongst an area where there is a lot of
industrial/ open storage LR, overall this LR is considered to have medium sensitivity. |
|||||
9.4 |
Other Agricultural Lands
in KTN |
Medium |
Medium |
Medium |
Medium |
This LR sits outside the works area and will not be affected. This LR refers to several small and fragmented agricultural lands in
different locations within the study area of KTN, including Chau Tau Tsuen,
Pak Shek Au, Yin Kong, Kam Tsin and Tai Tau Leng. Most of these agricultural lands have been
wholly or partly abandoned and grass and shrubs now grow in the fields. For those fields remaining active, common
crops cultivated by farmers include Brassica
parachinensis and Lactuca sativa. |
|||||
This LR has low to medium value in terms of crop production and is
relatively tolerant to change. It is
considered to have medium
sensitivity. |
|||||
9.5 |
Other Orchards
Areas in KTN |
Medium |
Medium |
Medium |
Medium |
This LR refers to several small and fragmented orchard areas in
different locations within the study area of KTN, including around the Ma Tso
Lung area, on the lower slopes of Fung Kong Shan, and near Ngam Pin. Common fruit trees in this LR include Musa x paradisiaca, Artocarpus macrocarpon, Mangifera indica
and Dimocarpus longan, where the
fruit trees present include Artocarpus
macrocarpon, Dimocarpus longan
and Carica papaya. Not all these orchard areas are still well
looked after and some have been left untreated for a while. |
|||||
This LR has medium value in terms of crop production and being
agricultural is relatively tolerant to change although trees generally take
longer to grow and produce than crops so ability to accommodate change is
medium. Overall this LR is considered
to have medium sensitivity. |
|||||
KLR 12 – Rural
Development Area |
|||||
Refers to traditional
villages, modern villages and small scale, low rise residential areas of
lower density dominated by domestic structures (mainly of 2-3 stories)
interwoven with roads and paths, but limited other infrastructure. There are some Ancestral Halls, shrines and
temples, and this LR may also contain limited facilities such as small police
stations, post offices, and covered water reservoirs and pumping stations and
some small, managed, recreational areas (such as football and basketball
pitches) and small wasteland areas either wholly or partly covered by weedy
or sparse vegetation. This LR often
has small orchard areas associated with it (most commonly planted fruit tree
species are Dimocarpus longan, Litchi
chinensis, Clausena lansium, Mangifera indica and Citrus maxima) and private gardens, as well as amenity planting
among the built structures. This LR
usually occurs in fragmented patches with agricultural or natural landscape
resources adjacent to it. |
|||||
Within the Study
Area of the KTN NDA (DP5) this LR is mainly
found in Ho Sheung Heung, Long Valley, Ngam Pin, along Fanling Highway, as
well as in the central area of Kwu Tung.
This LR also includes water reservoir and rifle range. |
|||||
12.1 |
Ho Sheung Heung
Rural Development Area |
Medium |
Medium |
Low |
Medium |
Ho Sheung Heung village is bounded by Ho Sheung Heung Pai Fung Road
and Chung Kuk Path. In the vicinity
(but not part of this LR), there is Ho Sheung Heung Fung Shui Woodland and
agricultural land in which water ponds are scattered. Although the village could be classified as
relatively modern due to the fact many houses have been replaced by modern
housing blocks of 2-3 storeys, some of the residential houses are identified
as Historic Buildings (refer to Chapter 11),
with Hau Kui Shek Ancestral Hall, a Declared Monument, located on the middle
of the village and two Grade 3 listed buildings, Hung Hing Temple & Pail
Fung Temple and ‘Sin Wai Nunnery’ located in the south of the village. The whole village is mostly hard-surfaced
and has limited softscape treatment but does include some trees (e.g. Dimocarpus longan, Litchi chinensis and Clausena lansium) and private amenity
planting (e.g. Plumeria rubra and Thuja orientalis). |
|||||
Although most of the houses in Ho Sheung Heung Village are relatively
modern, the ancestral hall and graded historic buildings are vulnerable to
change since they cannot be easily recreated and overall this LR has medium sensitivity. |
|||||
12.2 |
Rural Development
Area in Long Valley, Yin Kong, Tsung Pak Long and Hak Ka Wai |
Medium |
High |
Low |
High |
This LR sits outside the works area and will not be affected. This LR lies between the Shek Sheung River and Fanling Highway to the
southeast of Long Valley. It covers
three villages: Yin Kong Village, Hak Ka Wai and Tsung Pak Long. |
|||||
Yin Kong Village is a traditional village undergoing
transformation. Some of the existing
residential houses in the northern part of the village are identified as
historical buildings. Earth shrines associated with Fung Shui Trees (Ficus microcarpa in most cases) are
present including the Grade 2 listed Earth God Shrine of Kam Tsin historic
building. In addition an old western
styled Enchi Lodge (Grade 2 historic building) is located on the southern
part of the village. Between the
northern and southern parts of the village there is grassland which would
have been agricultural land in the past.
On the other hand, the modern aspect of Yin Kong Village is presented
by many well-established modern village houses as well as facilities such as
small-scaled playgrounds. |
|||||
Hak Ka Wai is a traditional village with around 100 years of
history. It consists of two rows of
residences, an ancestral hall (the Wong Shek Chung Ancestral Hall), a study
hall, an entrance gate, enclosing walls and a watch tower. This village is a Grade 1 historic
building. |
|||||
Tsung Pak Long is a traditional village undergoing
transformation. It contains ancestral
halls, earth shrines, a school and a church in traditional style to its
northwest. Most areas within this LR
are hard-surfaced and have limited vegetation except those private amenity
plantings, in which fruit trees Dimocarpus
longan, Carica papaya and Citrus reticulata and landscaping
shrub Duranta erecta and Murraya paniculata are commonly found. |
|||||
The historic buildings located in this LR, particularly the relatively
large area of Hak Ka Wai village, cannot be easily recreated and this LR is
relatively intolerant to change.
Overall it is considered to have high
sensitivity. |
|||||
12.9 |
Rural Development
Area in Shek Tsai Leng, Tong Kok, Fung Kong and Tit Hang |
Medium |
Medium |
Medium |
Medium |
This LR sits outside the works area and will not be affected. Rural area in Shek Tsai Leng mainly includes Dills Corner Garden and its
associated facilities. Dills Corner
Garden is located along Po Lau Road and is a home for the aged. It contains several rows of 2-storey houses and is enclosed by
fences. Except for several individual,
large trees along the fences (mostly Ficus
microcarpa), this area is almost entirely hard-surfaced with limited
landscaping. Nevertheless, well
maintained trees are planted along the roads in this area and dominant
species include Acacia confusa and Melaleuca quinquenervia. There is also
a soccer pitch, playground and school in this area. |
|||||
The rural area in Tong Kok, Fung Kong and Tit Hang contains loosely
grouped village houses in traditional style, with some graves of Hau clan
scattered in the northern part of Fung Kong Tsuen. All the villages are mostly hard-surfaced
with small houses and winding paths and have limited softscape treatment but
do include some abandoned fruit trees (e.g. Dimocarpus longan, Citrus
maxima, Musa x paradisiaca and Clausena lansium) and private amenity planting. |
|||||
This is a LR with a medium capacity to tolerate change and its
sensitivity is considered to be medium. |
|||||
12.10 |
Lo Wu Rifle Range |
Medium |
Medium |
Medium |
Medium |
This LR sits outside the works area and will not be affected. Lo Wu Rifle Range is located between Fung Kong Shan and the Tai Shek
Mo mountain. It is a large piece of
grassland for military purpose. Many
mature trees grow naturally in the surroundings, including Bauhinia blakeana, Macaranga tanarius,
Celtis sinensis and Leucaena
leucocephala. |
|||||
This LR is a man-made area but it is green
land not hard surface and so has a medium tolerance to change. The sensitivity of this LR is medium. |
|||||
12.11 |
Rural Development Area in Ma Tso Lung |
Low to Medium |
Medium |
Low |
Medium |
This LR sits outside the works area and will not be affected. This LR refers to the rural area at Ma Tso Lung on the northwest of
the KTN NDA Study Area. It mainly
covers two villages, i.e. Ma Tso Lung San Tsuen and Shun Yee San Tsuen, which
are relatively small, mainly consisting of more traditional houses of a
single storey. Trees associated with
this area include some fruit trees such as Diospyros kaki, Musa x
paradisiaca and Dimocarpus longan
as well as other native and exotic trees such as Bauhinia blakeana, Leucaena
leucocephala, and Bombax ceiba. |
|||||
Although these structures cannot be recreated easily and have low
ability to accommodate change, their landscape quality and maturity are not
high and overall this LR has medium
sensitivity. |
|||||
KLR 13 - Industrial / Open Storage |
|||||
Refers to areas which are heavily adapted for human industrial use,
such as factory facilities, waste processing plants and other industrial
buildings, often with some open areas for storage, parking or other
associated activities. There is very
little existing vegetation within this LR. |
|||||
Within the Study Area of KTN NDA, this LR is mainly found in areas
adjacent to villages and main roads, such as Yin Kong industrial / open
storage, Shek Tsai Leng, Tong Kok and Fung Kong open storage and Pak Shek Au
open storage. It also includes Sheung
Shui Slaughter House, Sheung Shui Water Treatment Works and Shek Wu Hui
Sewage Treatment Works. This LR can
also be found at the foothill of more natural LRs, often on flatter land and
includes Ki Lung Shan Foothill industrial / open storage. |
|||||
13.2 |
Industrial / Open
Storage Area in Yin Kong |
Low |
Low |
High |
Low |
This LR sits outside the works area and will not be affected. This is an isolated plot beside Yin Kong Village and is now mainly
used for open storage and car park.
Trees growing within this LR include Macaranga tanarius, Ficus microcarpa, Celtis sinensis, Araucaria heterophylla, Carica papaya, Artocarpus macrocarpon and
Syzygium jambos. |
|||||
This LR predominantly consists of man-made structures which have a high
capacity to tolerate change and have low landscape value. This LR is considered to have low sensitivity. |
|||||
13.3 |
Industrial/Open
Storage in Shek Tsai Leng, Tong Kok and Fung Kong |
Low |
Low |
Medium |
Low |
This LR sits outside the works area and will not be affected. This LR is located around the villages of Shek Tsai Leng, Fung Kong
and Tong Kok and is generally in the middle of the KTN NDA Study Area. This continuous area is largely used for
open storage and car parks and has a network of small road running within it,
some with associated concrete drainage channels. It also has several waste processing plants
within this LR. In addition, this LR
has two graded historic buildings, one just west of where the Sheung Yue
River flows under Fanling Highway (Yeung Yuen Grade 3 listed building) and
one in Shek Tsai Leng (Yan
Wah Lo Grade 3 listed building). (Further
details can be found in Chapter 11). |
|||||
Trees within this LR are not actively
managed and grasses occupy many places between the car parks. Tree species commonly found in the area
include Macaranga tanarius, Celtis
sinensis, Bauhinia blakeana, Mallotus paniculatus, Ficus microcarpa, Acacia
confusa, Casuarina equisetifolia, Leucaena leucocephala, Hibiscus tiliaceus,
Dimocarpus longan, Livistona chinensis, Morus alba, Psidium guajava and Artocarpus macrocarpon. This LR predominantly consists of man made structures which have a
high capacity to tolerate change and have low landscape value. The exceptions are the two graded historic
buildings which have low ability to change and are rarer, but since they form
a very small part of this LR, overall it is considered to have low sensitivity. |
|||||
KLR 14 – Major Transportation Corridor |
|||||
Refers to Fanling Highway running west-east
along the south of the Study Area, all the associated major intersections and
key adjacent roads including Castle Peak Road. There is tree planting along
the sides of the roads consisting of a variety of indigenous and exotic
species. In addition, there is some planting along the central divider
(median) in some sections, including of amenity shrubs. Drainage channels associated with the
roads/highway are considered part of this LR as they are an integral function
of the roadscape. |
|||||
14.1 |
Fanling Highway and nearby associated roads. |
Medium |
Medium |
Medium |
Medium |
This LR sits outside the works area and
will not be affected. This LR is includes the Fanling Highway (Kwu Tung section), Castle
Peak Road running parallel and nearby associated roads, which are the major
transportation routes connecting Kwu Tung to its adjacent areas. The roads run west-east along the south of
the Study Area and there are areas of established roadside planting along the
sides of the roads as well as in the central divider (median) in some
sections, including of amenity shrubs.
In addition along parts of the roads, there are open drainage channels
lined by the roadside planting. Trees
commonly used for roadside planting in this area include Melaleuca quinquenervia, Bombax
ceiba, Ficus microcarpa, Casuarina equisetifolia, Acacia confusa and Bauhinia blakeana. |
|||||
Despite being a man-made resource, the landscape value of this LR is
increased by the significant roadside planting; a single OVT also sits within this area
but considered separately (See KLR-5.4).
The overall sensitivity is considered to be medium |
Table 12B.3.2 - Landscape Character Areas and their
Sensitivity- KTN NDA (DP5)
Id No. |
Landscape
Character Area (LCA) |
Quality &
Maturity |
Rarity |
Ability to
Accommodate Change |
Sensitivity |
KLCA-1 |
Natural Hillside
Landscape |
High |
High |
Low |
High |
This LCA sits outside the works area and will not be affected. Refers to large hillside areas which are dominated by shrubland,
grassland and some woodland in places. |
|||||
Within the Study Area for KTN NDA this LCA encompasses Tai Shek Mo
(183 mPD), Western Range of Tai Shek Mo (Ma Tso Lung and Lok Ma Chau) (144 mPD),
Ki Lun Shan (222 mPD), and Fung Kong Shan (40 mPD). |
|||||
Tai Shek Mo lies to the north of the Study Area. The primary ridgeline extends southward
while the Western Range ridgeline runs approximately NE-SW, covering Ma Tso
Lung and Lok Ma Chau. These two sections of LCA are separated by lower land
and to their south the smaller Fung Kong Shan is found. |
|||||
Ki Lun Shan lies to the south west of the Study Area. |
|||||
This landscape area is natural and has high landscape quality. Its significance is also high and it is not
capable tolerate to change. Therefore
its sensitivity is considered to be high.
|
|||||
KLCA-2 |
Rural and Urban
Peripheral Village Landscape |
Medium |
Low |
Medium |
Medium |
Refers to rural village areas and village areas on the fringes of
urban developments, including relic landscapes of former villages. This LCA is dominated by small or medium
sized villages with modern and traditional houses and some Ancestral Halls,
interspersed with small agricultural plots and comprises a broad mix of other
land uses including water ponds, schools, sports grounds, and playgrounds,
some open storage areas and car parks, and a golf course to the southeast of
Kwu Tung. This LCA also has some small
patches of woodland as well as vegetation associated with the villages and
park areas. |
|||||
Within the Study
Area for KTN NDA this LCA is found to the west near the San Tin Interchange,
in the east at the Shek Sheung River and the area east of this river, and
more centrally bordering Ma Tso Lung Road, Shek Tsai Leng and east of Fung Kong Shan. |
|||||
This LCA is considered to have medium tolerance to change and moderate
amenity value. Its sensitivity is
therefore medium. |
|||||
KLCA-4 |
Industrial Landscape |
Low |
Low |
High |
Low |
This LCA sits outside the works area and will not be affected. Refers to areas comprising a broad mix of land uses including
factories, utility facilities, workshops, open storage and some channelized
water courses. It is normally located
on low lying ground or at the base of hills and may include small and
fragmented areas of residential houses and their associated agricultural
land. There is little significant
vegetation among this built environment, but small patches of vegetation do
exist, particularly along the channelized river. |
|||||
Within the Study Area for KTN DPs this LCA is found to the west near
the San Tin Interchange, in the east at the Shek Sheung River and the area
east of this river, and more centrally bordering Ma Tso Lung Road, Shek Tsai Leng and east of Fung Kong Shan. |
|||||
This LCA usually contains abandoned facilities that are able to
accommodate change. Except for the
significant planting along the Ng Tung River, most areas in this LCA have
little vegetation, resulting in a low landscape amenity. Therefore, its sensitivity is considered to
be low. |
|||||
KLCA-5 |
Lowland Agricultural Landscape |
Medium |
Medium |
Low |
High |
Refers to large areas
dominated by cultivated land with scattered small villages and low-rise
buildings and may also include some fishponds and irrigation ponds.
This LCA is mostly found among lowlands and floodplain areas. |
|||||
Within the Study Area the key area of this LCA is found at Long Valley
which is a highly sensitive LR in itself. And there are also some
isolated farmlands at Chau Tau and Ma Tso Lung. Tree vegetation is
generally sparse and restricted to field boundaries, adjacent to local houses
and, together with bamboo, along the banks of Sheung Yue River. The value and
significance of the LCA is high, largely due to it encompassing the high
quality, contiguous agricultural land of the core Long Valley area. It
has little tolerance to change and its sensitivity is considered to be
high. |
|||||
KLCA-6 |
Major Transportation Corridor Landscape |
Medium |
Medium |
Medium |
Medium |
This LCA sits outside the works area and will not be affected. Refers to major highway and railway areas, with their scattered
associated buildings. Within the Study Area for KTN DPs, Fanling Highway is a major
transport route stretching in an east west direction located at the south
boundary of the Study Area. It has two
key connection junctions at Fan Kam Road to the east and San Sham Road to the
west. In addition, the MTRC East Rail
leading to the Lo Wu Station runs south-north in the east of the study area. Lok Ma Chau Spur Line branches off from
Sheung Shui Railway Station to Lok Ma Chau Station, of which this
section is underground passing through KTN NDA. The resource is considered to be highly tolerance to change and its
sensitivity is medium. |
|||||
KLCA-7 |
Major Water Course Corridor Landscape |
Medium |
High |
Medium |
Medium |
This LCA sits outside the works area and will not be affected. Refers to modified water courses channelised with concrete or
grasscrete and also includes the vegetation associated with the water course,
both within the channel and along the banks as well as in the ridge of the
banks. Within the Study Area of KTN NDA this LR includes the Ng Tung River,
Sheung Yue River and Shek Sheung River. The landscape amenity and significance of this LCA are medium to
high. Due to its partially artificial
state, it is relatively tolerant to change and its sensitivity is considered
to be medium. |
12B.3.1 Summary of baseline conditions
The LRs within the study area which have been recognised for their higher sensitivity are predominantly natural streams, woodland, marsh/ wetland, selected water ponds. Other resources such as agricultural land and rural development areas may also have high sensitivity due to certain elements or characteristics such as quality of the environment, maturity of landscape planting or historically significant buildings/structures. The baseline conditions for LRs or DP Package B are summarised below.
LRs associated with water are generally considered to have a higher landscape value. In this case those at Ma Tso Lung (KLR-2.4) are rated high sensitivity. This rating takes into account the entirety of the water course and the nature of the stream in relation to whether the channel is mainly natural, its seasonality of flow or whether it has sections which have been altered by human activity. The streams in Kwu Tung (KLR-2.1) were generally natural but degraded by pollution, with seasonal flows and some sections fortified by concrete banks such that they were considered less sensitive and rated ‘medium’.
Similarly to watercourses, ponds and marsh/wetland are generally considered a valuable landscape resource as many incorporate natural planting, strengthen rural character and have strong cultural connections in terms of agricultural production and land use pattern. Ponds located at Ho Sheung Heung (KLR-3.1), in Long Valley associated with agriculture (KLR-3.2) and within the closed area (KLR-3.8) are all considered as having ‘high’ sensitivity. In addition all the marsh/wetland areas including those in Long Valley (KLR-4.1) and the mitigation wetland along the Sheung Yue River (KLR-4.2) and Wetland/ Marsh in the Closed Area (KLR-4.3) are all rated with high sensitivity.
Trees are considered as precious LRs which have a vital role in landscape character, diversity, naturalness and maturity of a landscape. As a result all areas of woodland within the NDA (both hillside and lowland) are rated as having ‘high’ sensitivity including Hillside Woodland in Ma Tso Lung, Tit Hang and Fung Kong (KLR-6.3), Ho Sheung Heung Fung Shui Woodland (KLR-6.4) and Lowland Woodland in Pak Shek Au and Tong Kok (KLR7.3). In addition, the five OVTs located within the roadside planting near Fanling Highway and Castle Peak road are highly sensitive due to their maturity; one of these OVTs (reference number LCSD N/45) sits within the study area of DP5. Scattered, isolated and small patches of man-made plantation are considered to be less valuable and therefore less sensitive.
KLR8-Shrubland/Grassland Mosaic surrounds the study area, associated with the local hillsides and prominences such as Shrubland/Grassland Mosaic in Tai Shek Mo and the Western Range Foothills (KLR-8.3). These LR are generally located on undeveloped areas of natural topography however they are managed using periodic fires, therefore their overall sensitivity is considered to be medium.
While most agricultural LRs have medium sensitivity due to their varying quality and use (vacant or in-use), the agricultural land in Long Valley (KLR9.1) is a large contiguous area which would be difficult to recreate in Hong Kong due to a lack of similar areas, this agricultural land is therefore recognised as having high sensitivity.
Most rural development areas (KLR12) are identified in having a medium sensitivity as a result of varying quality of built form, vegetation cover and hard landscape treatments. The rural development area in Long Valley, Ying Kong, Tsung Pak Long and Hak Ka Wai has a number of historical buildings within it, with the whole of Hak Ka Wai village is designated as Grade 1 historic building. This KLR-12.2 is therefore considered to be more sensitive that other rural development areas and has ‘high’ sensitivity.
It should also be noted that there is a considerable amount of open storage/ industrial land within the Study Area which is highly degraded in terms of landscape quality and changeable in terms of characteristics; all of these areas are considered of low quality and sensitivity.
With regards to LCAs, Natural Hillside Landscape (KLCA-1) is considered highly sensitive, largely due to its high landscape quality and inability to accommodate change. The Lowland Agricultural Landscape encompassing the Long Valley area (KLCA-5) similarly has high sensitivity given it includes a large contiguous area of high quality agricultural land in the Long Valley area (see KLR-9.1) and has a low ability to accommodate change. Rural and Urban Peripheral Village Landscape (KLCA-2) and Major Water Course Corridor Landscape (KLCA-7) have medium sensitivity, largely due to their moderate amenity value and the Major Transport Corridor Landscape (KLCA-6) also has medium sensitivity mainly due to the extensive planting along the Fanling Highway and Castle Peak Road conferring high greening and lowering this LCA’s ability to accommodate change. Industrial Landscape (KLCA-4) has low sensitivity due to their low landscape quality and high ability to accommodate change.
DP 5 relates to the construction of 2no. Sewage Pumping Stations in the KTN NDA, these are located:
· To the south of Ma Tso Lung Shun Yee San Tsuen Village, north of the KTN NDA.
· South of Ho Sheung Heung Village.
In both cases, the construction of the SPS will require the direct loss of Agricultural land and associated shrubland vegetation cover. The SPS building will be approximately 5m high surrounded by solid walling at approximately 3m high. The footprint of both buildings is 15x10m.
During the construction of the various components of DP 5, potential landscape and visual impacts will generally result from the following:
· Site clearance including clearance of vegetation.
· Site formation works including excavations for foundation and construction of utility pits / connections
· Stockpiling of construction materials, including existing topsoil, and storage of construction equipment and mechanical plant.
· Construction of Sewage Pumping Station Buildings, internal access road and pedestrian access, boundary walling/fencing
· Temporary structures within the Project Site including boundary fencing/hoarding and parking areas.
· Alteration to natural terrain.
During the operation phase, potential impacts will result from the following:
· Operation of new Sewage Pumping Stations.
· Residual impacts from loss of trees and vegetation during the construction phase.
The landscape impact assessment has been carried out taking into consideration the baseline LRs and LCAs described in Section 12B.3 and potential impacts described in Section 12B.4 and 5.
Further details of the potential landscape impacts are provided for each DP below.
The magnitude of change on KTN DP 5 LRs and LCAs are presented in Tables 12B.6.1 and 12B.6.2 below.
Landscape Impacts are mapped on Figure 12.52.21 and 12.52.32.
Table
12B.6.1 Magnitude of Change on LRs (DP 5)
Note - For LRs where no impact is recorded, these are omitted.
Name |
DPs and Site No. (Land Use Type) Impacting LR |
Area of LR within study area and within DP boundary (ha) or length (m or
Km) |
Physical extent of the impact (Small/ Medium/ Large) |
Compatibility with Surrounding Landscape |
Duration of Impact |
Reversibility of Change |
Magnitude of Change |
||||||||||
Construction |
Operation |
Construction |
Operation |
Construction |
Operation |
Construction |
Operation |
||||||||||
KLR 1 |
Channelized Water
Course |
||||||||||||||||
1.3 |
Sheung Yue River |
DP5: New Sewage Pumping Stations |
Study Area: 9.6ha / 1.12km SP Boundary 0.003ha / 50m |
Small |
Fair |
Fair |
Temporary Short Term |
Permanent |
Reversible |
Reversible |
Small |
Small |
|||||
Description of Key Impacts during Construction and Operation DP 5 – SPS South of Ho Sheung Heung The new DP will be built close the river frontage. A small section of the upper engineered
river bank, forming part of the existing access track would be affected by
the proposed construction works. Minor
vegetation clearance works would be required as well as breaking out of hard
surfacing. Given the previous engineering works within this area as part of the
river channelisation, the compatibility of the works is considered to be fair
in construction and operation. As a result of the
very small scale of the impacted area and the man-made nature of the piece of
landscape affected, the overall magnitude of change for this LR is considered to be small during both construction
and operation. |
|||||||||||||||||
KLR 8 |
Shrubland/ Grassland Mosaic |
||||||||||||||||
8.3 |
Shrubland/ Grassland Mosaic in
Tai Shek Mo and the Western Ranges Foothills |
DP5: New Sewage Pumping Stations |
Study Area: 38ha DP Boundary 0.27ha |
Small |
Poor |
Poor |
Temporary Short Term |
Permanent |
Reversible |
Irreversible |
Small |
Negligible |
|||||
Description of Key Impacts during Construction and Operation Shrubland vegetation would be cleared and the works area filled to
raise the formation level up to the correct height. Boundary walling will be erected together with
internal area of hard standing for vehicular access within the compound. The SPS building will be housed within this
compound area. The construction would replace the semi-natural vegetation cover with
a building and associated compound area involving a permanent loss of the LR;
in this case the compatibility during construction and operation is
considered to be poor. As a result of the overall small scale of the works and the large
scale abundance of the LR in the wider landscape, the magnitude of change is
considered to be small in construction and negligible in operation. |
|||||||||||||||||
KLR 9 |
Agricultural Land |
||||||||||||||||
9.3 |
Agricultural Lands in Shek Tsai Leng, Tong
Kok and Fung Kong |
DP5: New Sewage
Pumping Station |
Study Area: 9.4ha DP Boundary: 0.22ha |
Small |
Poor |
Poor |
Temporary Medium
Term |
Permanent |
Reversible |
Irreversible |
Small |
Negligible |
|||||
|
Description of Key Impacts during Construction and Operation DP 5 – SPS South of Ho Sheung Heung A small area of agricultural land would be cleared and the works area
filled to raise the formation level up to the correct height. Boundary walling will be erected together
with internal an area of hard standing for vehicular access within the
compound. The SPS building will be housed within this compound area. The construction would replace the semi-natural vegetation cover with
a building and compound area; in this case the compatibility during
construction and operation is considered to be poor. As a result of the overall scale of the works located on the fringe of
this LR, the magnitude of change is considered to be small in construction
and negligible in operation. |
||||||||||||||||
9.5 |
Other Orchards in KTN |
DP5: New Sewage Pumping Station |
Study Boundary 2.9ha DP Boundary 0.003ha |
Small |
Fair |
Good |
Temporary Short
Term |
Permanent |
Reversible |
Irreversible |
Negligible |
Negligible |
|||||
|
Description of Key Impacts during Construction and Operation DP 5 – SPS South of Ma Tso Lung An extremely small area of orchard would be affected; at most some
minor clipping of trees may be required in terms of overhang tree limbs into
the site area. In addition some minor
earthworks may be required in order to construct a level foundation for the
proposed pumping station. Given the
small scale nature of the works, the compatibility during construction is
considered to be fair. In operation
the works will affect only a small area on the periphery of this resource
therefore the compatibility is considered to be good. The construction are is very small and will have limited impact on the
LR therefore the magnitude of change during construction and operation is
considered to be negligible. |
||||||||||||||||
KLR 12 |
Rural Development
Area |
||||||||||||||||
12.1 |
Ho Sheung Heung
Rural Development Area |
DP5: New Sewage
Pumping Station |
Study Boundary 11.23ha DP Boundary 0.008ha |
Small |
Good |
Good |
Temporary Short Term |
Permanent |
Reversible |
Irreversible |
Negligible |
Negligible |
|||||
Description of Key Impacts during Construction and Operation DP 5 – SPS South of Ho Sheung Heung A very small area of this LR will be affected by site formation. Given the previously development nature of
this LR and small area concerned the compatibility of the works during
construction and operation are considered to be good. Again, due to the very small area concerned and good compatibility,
the magnitude of change is considered to be negligible during construction
and operation. |
|||||||||||||||||
Table 12B.6.2 Magnitude of Change on LCAs (DP5)
Note - For LCAs where no
impact is recorded, these are omitted.
LCA Code |
Name |
Site No. (Land Use Type*) Impacting LCA |
Area of LCA affected within DP boundary
(ha) (Approx. percentage of this impacted) |
Physical extent of the impact (Small/ Medium/ Large) |
Compatibility with Surrounding Landscape |
Duration of Impact |
Reversibility of Change |
Magnitude of Change |
||||
Construction |
Operation |
Construction |
Operation |
Construction |
Operation |
Construction |
Operation |
|||||
KLCA-2 |
Rural and Urban Peripheral Village Landscape |
This LCA is affected by site: DP 5: New Sewage Pumping Station |
Study Area: 84.4ha DP Boundary 0.17 |
Small |
Fair |
Fair |
Temporary Short Term |
Permanent |
Reversible |
Irreversible |
Negligible |
Negligible |
|
|
Description of Key Impacts during Construction and Operation Construction of
the SPS would require vegetation clearance and cut and fill work to raise the
formation level up to the correct height.
Boundary walling will be erected together with internal an area of
hard standing for vehicular access within the compound. The SPS building will be housed within this
compound area. The construction
would replace the semi-natural vegetation cover with a building and
associated compound footprint; in this case the compatibility during
construction and operation is considered to be fair given the developed
nature of the LCA. As a result of
the overall scale of the works and the limited impact this would have on the wider
LCA, the magnitude of change is considered to be negligible in both
construction and operation. |
||||||||||
KLCA-5 |
Lowland Agricultural Landscape |
This LCA is affected by site: DP 5: New Sewage Pumping Station |
Study Boundary: 48.7ha DP Boundary 0.36ha |
Small |
Poor |
Poor |
Temporary Short Term |
Permanent |
Reversible |
Irreversible |
Negligible |
Negligible |
|
|
Description of Key Impacts during Construction and Operation DP 5 – SPS South
of Ma Tso Lung Construction of
the SPSs would require vegetation clearance and cut and fill work to raise
the formation level up to the correct height.
Boundary walling will be erected together with internal an area of
hard standing for vehicular access within the compound. The SPS building will be housed within this
compound area. The construction
would intrude into this relatively undeveloped open landscape area and replace a piece of farmland, it is
therefore considered to have poor compatibility during construction and
operation. As a result of
the overall scale of the works and the limited impact this would have on the
wider LCA, the magnitude of change is considered to be negligible in both
construction and operation. |
A summary of the key landscape impacts identified in Table 12B.6.1 and 2 for both SPS is provided below.
DP 5 - New sewage pumping stations (SPS) in KTN NDA
The principal impacts as a result of the SPS construction works will
occur during the construction stage. The
following LRs/LCAs are affected:
SPS South of Ho Heung Sheung
KLR-1.3 Sheung Yue River
KLR-9.3 Agricultural Lands in Shek Tsai Leng, Tong Kok and Tung Fong
KLR-12.1 Ho Sheung Heung Rural Development Area
KLCA-5 Lowland Agricultural Landscape
It is predicted that a small impact will be generated in relation to KLR 9.3 which forms the majority of the works area. Vegetation clearance and earthworks will be required, resulting in a small loss of the associated LR area. The impacts within KLR 1.3 and 12.1 are negligible. As a result of the very small nature of the works, there will be negligible impacts in relation to LCA-5.
SPS South of Ma Tso Lung
KLR- 8.3 Shrubland/Grassland Mosaic in Tai Shek Mo and the Western Range
Foothills
KLR-9.5 Other Orchards in KTN
KLCA-2 Rural and Urban Peripheral Village Landscape
KLCA-5 Lowland Agricultural Landscape
It is predicted that a small impact will be generated in relation to KLR 8.3 which forms the majority of the works area. Vegetation clearance and earthworks will be required, resulting in permanent loss of the associated LRs/LCA area. The impacts within KLR 9.5 are negligible. In addition, the impacts on KLCA-2 and 5 are also negligible due to the very limited extent of the works.
The potential significance of landscape impacts during the construction and operational phases, before mitigation, is provided in Tables 12B.8.1 and 12B.8.2 for DP 5. The assessment follows the methodology proposed in Section 12.18 and the matrix provided in Table 12.18.1.
Landscape Impacts are mapped on Figure 12.52.21 and 12.52.32
Table
12B.8.1 Significance of landscape impacts on LRs (DP5)
LR Code |
Name |
LR Sensitivity (High/ Medium/ Low) |
Magnitude of Impact (Large/ Intermediate/ Small/ Negligible |
Impact Significance BEFORE Mitigation (Substantial/ Moderate/ Slight/
Insignificant) |
||
Construction |
Operation |
Construction |
Operation |
|||
KLR 1 |
Channelized
Water Course |
|||||
1.3 |
Sheung Yue River |
Medium |
Small |
Small |
Slight |
Slight |
KLR 8 |
Shrubland/Grassland
Mosaic |
|||||
8.3 |
Shrubland/Grassland Mosaic in Tai Shek Mo and the Western Range
Foothills |
Medium |
Small |
Negligible |
Slight |
Insignificant |
KLR 9 |
Agricultural
Land |
|||||
9.3 |
Agricultural Lands in Shek Tsai Leng, Tong Kok and Fung Kong |
Medium |
Small |
Negligible |
Slight |
Insignificant |
9.5 |
Other Orchards in KTN |
Medium |
Negligible |
Negligible |
Insignificant |
Insignificant |
KLR 12 |
Rural
Development Area |
|||||
12.1 |
Ho Sheung Heung Rural Development Area |
Medium |
Negligible |
Negligible |
Insignificant |
Insignificant |
In summary for the LRs, slight adverse impacts are
predicted at the construction stage for KLR1.4
Sheung Yue River, KLR 8.3 Shrubland/ Grassland Mosaic in Tai Shek Mo and the Western Range
Foothills and KLR 9.3 Agricultural Lands in Shek Tsai Leng and Fung Kong due to
vegetation clearance, earthworks works and subsequent construction of both
SPSs. Due to the very small footprint of
the works, impacts during the operational stage are considered to be slight to
KLR 1.4 and insignificant to KLR 8.3 and 9.3.
The remaining LRs will all experience insignificant impacts at the construction and operational stage due to minimal interference as a result of the construction works.
Table 12B.6.2 Significance
of Impacts on LCAs (DP5)
LCA Code |
Name |
LCA Sensitivity (High/ Medium/ Low) |
Magnitude of Impact (Large/ Intermediate/
Small/ Negligible |
Impact Significance BEFORE Mitigation
(Substantial/ Moderate/ Slight/ Insignificant) |
||
Construction |
Operation |
Construction |
Operation |
|||
KLCA 2 |
Rural and Urban Peripheral Village
Landscape |
Medium |
Negligible |
Negligible |
Insignificant |
Insignificant |
KLCA 5 |
Lowland Agricultural Landscape |
High |
Negligible |
Negligible |
Insignificant |
Insignificant |
In summary for the LCAs, insignificant impacts are predicted during the construction and operational stage in relation to KLCA 5 Lowland Agricultural Landscape andKLCA-2 Rural and Urban Peripheral Village Landscape. In both cases the construction footprint is very small and will have a limited influence on the surrounding LCAs.
The proposed mitigation measures for the Project are described in the following section and summarised in Table 12B.9.1 below. The same table also lists the agents responsible for the capital funding, the implementation and the maintenance of the suggested measures. These agents will be agreed before the start of construction. Mitigation measures which are not relevant to this DP have been omitted.
Table 12B.9.1 - Summary of Proposed
Mitigation Measures
Mitigation Measure Code |
Summary Description |
Capital Funding Agency |
Implementation Agency |
Post-Construction Maintenance Agency ([1]) |
MM1 |
Minimum
Topographical Change |
Government |
Contractors of the
Government |
n/a |
MM2 |
Detailed Design - Visual |
Government |
Contractors of the
Government |
DSD |
MM4 |
Tree Protection & Preservation |
Government |
Contractors of the Government |
n/a |
MM5 |
Tree
Transplantation |
Government |
Contractors of the Government |
DSD |
MM6 |
Slope
Landscaping |
Government |
Contractors |
DSD |
MM7 |
Compensatory
Planting |
Government |
Contractors of the Government |
DSD |
MM9 |
Vertical
Greening |
Government |
Contractors of the Government |
DSD |
MM10 |
Green Roof |
Government |
Contractors of the Government |
DSD |
MM11 |
Screen
Planting |
Government |
Contractors of the Government |
DSD |
MM14.3 |
Watercourse
Impact Mitigation – Enhancement Planting
along Embankment |
Government/Private Section |
Contractors of the Government/Private Sector |
DSD/LCSD/AFCD |
MM16 |
Screen
Hoarding |
Government |
Contractors of the Government |
n/a |
MM17 |
Light
Control |
Government |
Contractors of the Government |
n/a |
Minimising Topographical Change (MM1)
To minimise landscape and visual impacts, the footprint and elevation of the proposed SPS have been be optimised to reduce potential topographical/ landform changes, as well as reduce land take and interference with natural terrain and reduce overall earth movements.
Detailed Design (Visual) (MM2)
The footprint of development components and the works area should also be kept to a practical minimum and the detailed design of development components for construction stage should follow the Sustainable Building Design Guidelines. The form, textures, finishes and colours of the proposed SPS buildings and boundary treatment should aim to be compatible with the existing surroundings. To improve visual amenity, designs should be aesthetically pleasing and treatment of structures also improve visual amenity. For example natural building materials such as stone and timber should be considered for architectural features, and light earthy tone colours such as shades of green, shades of grey, shades of brown and off-white should also be considered to reduce the visibility of the development components.
The treatment of the SPS facades and boundary should also reflect the materials and architectural styles of the surrounding proposed development in order to maximise visual integration.
Green roofs have also been recommended (See MM10).
Tree Protection & Preservation (MM4)
Exiting trees to be retained within the Project Site should be carefully protected during construction. Detailed Tree Protection Specification shall be provided in the Contract Specification. Under this specification, the Contractor shall be required to submit, for approval, a detailed working method statement for the protection of trees prior to undertaking any works adjacent to all retained trees, including trees in contractor’s works areas.
A detailed tree survey will be carried out for the Tree Removal Application (TRA) process which will be carried out at the later detailed design stage of the Project. The detailed tree survey will propose which trees should be retained, transplanted or felled and will include details of tree protection measures for those trees to be retained.
Tree Transplantation (MM5)
Trees unavoidably affected by the Project works should be transplanted where practical. Trees should be transplanted straight to their final receptor site and not held in a temporary nursery as far as possible. A detailed Tree Transplanting Specification shall be provided in the Contract Specification, where applicable. Sufficient time for necessary tree root and crown preparation periods shall be allowed in the project programme. A detailed transplanting proposal will be submitted to relevant government departments for approval in accordance with ETWBTC 2/2004 and 3/2006 and HyD HQ/GN/13 Interim Guidelines for Tree Transplanting Works under Highways Department's Vegetation Maintenance Ambit. Transplanted trees should be located as close as possible to the works area.
Slope Landscaping (MM6)
Site formation has been reduced as far as possible to avoid substantial slope cutting (also see MM1).
Hydroseeding of modified slopes should be done as soon as grading works are completed to prevent erosion and subsequent loss of landscape resources and character. Woodland tree seedlings and/ or shrubs should be planted where the slope gradient and site conditions allow. In addition, landscape planting should be provided for the retaining structures associated with modified slopes, where conditions allow. All slope landscaping works should comply with GEO Publication No. 1/2011-Technical Guidelines on Landscape Treatment for Slopes.
Compensatory Planting (MM7)
Compensatory tree planting for all felled trees shall be provided to the satisfaction of relevant Government departments. Required numbers and locations of compensatory trees shall be determined and agreed separately with Government during the Tree Felling Application process under ETWBTC 3/2006. Compensatory planting is proposed directly around the SPSs to tie in with MM11 proposals.
Vertical Greening (MM9)
Planting of climbers to grow up vertical surfaces were appropriate, such as along perimeter fencing/walling and building walls are recommended to break up uniform surfaces and provide visual amenity.
Green Roof (MM10)
Roof greening where appropriate should be established on proposed buildings to reduce exposure to untreated concrete surfaces and particularly mitigate visual impact to VSRs at higher elevations.
Screen Planting (MM11)
Tall screen/buffer trees and shrubs should be planted to screen proposed structures such as roads and buildings. This measure may additionally form part of the compensatory planting and will improve compatibility with the surrounding landscape.
Watercourse Impact Mitigation (MM14)
For channelized watercourses if these are modified, they should match the existing and include enhancement planting to upgrade the channels as appropriate, including consideration of wetland planting along embankments where appropriate.
Enhancement Planting along Embankment MM14.3
For channelised watercourses, if these are modified, the Drainage Services Department Practice Note No.1/2005 – Guidelines on Environmental Considerations for River Channel Design, should be considered and appropriate mitigation measures included ensuring the new watercourses match the existing as far as possible. Measures can include enhancement planting to upgrade the channels as appropriate, including consideration of wetland planting along embankments where appropriate; as well as consideration of the best materials for the channel lining (e.g. gabion). All measures must also ensure any necessary maintenance work can be carried out and that the channel meets all its requirements for water flow.
The proposed construction of the SPS south of Ho Sheung Heung will interface with the upper access track of the Sheung Yeung River. As stated above, the replacement channel works should match the existing and where possible include enhancement planting.
Screen Hoarding (MM16)
Screen hoarding shall be erected along areas of the construction works site boundary where the works site borders publically accessible routes and/or is close to visually sensitive receivers (VSRs), to screen undesirable views of the works site. It is proposed that the screening be compatible with the surrounding environment and where possible, non-reflective, recessive colours be used.
Light Control (MM17)
Construction day and night time lighting should be controlled to minimise glare impact to adjacent VSRs during the construction stage. Shrouded or directional lighting should be considered where appropriate as a general good practice construction measure but especially where works are in close proximity to residential VSRs.
Other good practise measures.
For areas unavoidably disturbed by the Project on a short term basis which will not undergo change as part of the DP (schedule 2 & 3 works), the general principle is to reinstate the area back to its original condition. Equally reinforced turf systems should be considered for appropriate areas such as car-parks or promenades.
With regard to topsoil, where identified, it should be stripped, treated appropriately, and where suitable and practical stored for re-use in the construction of the soft landscape works such as roadside amenity strips, and open space sites. It is assumed that the topmost 100mm of soil surface will be topsoil material. This good site practice and will also minimize off-site disposal.
For the all planting, this should be installed as soon as the areas become available, to achieve early establishment.
The proposed landscape and visual mitigation measures, as described in Section 12B.10, have been applied to the various impacts and used to identify potential residual impacts.
The potential significance of landscape impacts during the construction and operational phases, before and after mitigation at day 1 and year 10, are provided in Tables 12A.10.1 and 12A.10.2. The tables assume that the appropriate mitigation measures have been applied and that the full effect of the soft landscape mitigation measures would be fully realised and established after 10 years.
Where insignificant impacts have been identified, mitigation measures are still shown in the table as these would be applied as best practice in the construction and operational stages as part of a consistent design and construction approach.
Landscape mitigation measures are presented on Figures 12.52.61
& 62.
Table 12B.10.1 Residual Landscape Impact on Implementation of Mitigation Measures for LRs
LR Code |
Name |
Impact Significance BEFORE Mitigation (Substantial/ Moderate/ Slight/
Insignificant) |
Recommended Mitigation Measures |
Residual Impact Significance UPON Mitigation (Substantial/ Moderate/
Slight/ Insignificant) |
||||
Construction |
Operation |
Construction |
Operation |
Construction |
Operation Day 1 |
Operation Year 10 |
||
KLR 1 |
Channelized
Water Course |
|||||||
1.3 |
Sheung Yue River |
Slight |
Slight |
1, 14.3 |
4 |
Insignificant |
Insignificant |
Insignificant |
KLR 8 |
Shrubland/ Grassland Mosaic |
|||||||
8.3 |
Shrubland/Grassland
Mosaic in Tai Shek Mo and the Western Range Foothills |
Slight |
Insignificant |
1, 4, 5, 6, 7 |
4 |
Insignificant |
Insignificant |
Insignificant |
KLR 9 |
Agricultural Land |
|||||||
9.3 |
Agricultural Lands
in Shek Tsai Leng, Tong Kok and Fung Kong |
Slight |
Insignificant |
1, 4, 5, 7 |
4 |
Insignificant |
Insignificant |
Insignificant |
9.4 |
Other Orchards in
KTN |
Insignificant |
Insignificant |
1, 4 |
n/a |
Insignificant |
Insignificant |
Insignificant |
KLR 12 |
Rural
Development Area |
|||||||
12.1 |
Ho Sheung Heung
Rural Development Area |
Insignificant |
Insignificant |
1, 4, 5, 7 |
4 |
Insignificant |
Insignificant |
Insignificant |
Table 12B.10.2 Residual Landscape Impact on Implementation of Mitigation Measures for LCAs
LCA Code |
Name |
Impact Significance BEFORE Mitigation
(Substantial/ Moderate/ Slight/ Insignificant) |
Recommended Mitigation Measures |
Residual Impact Significance UPON Mitigation
(Substantial/ Moderate/ Slight/ Insignificant) |
||||
Construction |
Operation |
Construction |
Operation |
Construction |
Operation Day 1 |
Operation Year 10 |
||
KLCA-2 |
Rural and Urban Peripheral Village Landscape |
Insignificant |
Insignificant |
1, 4, 5, 7 |
4 |
Insignificant |
Insignificant |
Insignificant |
KLCA-5 |
Lowland Agricultural Landscape |
Insignificant |
Insignificant |
1, 4, 5, 7 |
4 |
Insignificant |
Insignificant |
Insignificant |
In summary, KLR 1.3 Sheung Yue River is predicted to experience slight adverse impacts prior to mitigation. It is considered that mitigation measures proposed which consist of minimising topographical change and enhancement planting along the embankment of Sheung Yue River, the significance of impact will reduce to insignificant in the construction and operation stage.
KLR 8.3 Shrubland/Grassland Mosaic in Tai Shek Mo and the Western Range Foothills is predicted to experience slight adverse impacts during construction, prior to mitigation. It is considered that mitigation measures which consist of preserving and protecting trees where possible, transplanting trees which cannot be retained insitu and compensating planting directly around the SPS will reduce this impact to insignificant in the construction and operational stage.
KLR 9.3 Agricultural Lands in Shek Tsai Leng, Tong Kok and Fung Kong are also predicted to experience slight adverse impacts during construction, prior to mitigation. It is considered that mitigation measures proposed which consist of minimising topographical change, preserving and protecting trees where possible, transplanting trees which cannot be retained insitu and compensating plating directly around the SPS will reduce this impact to insignificant in the construction and operational stage.
All other LR would experience insignificant impacts during construction and operation.
In terms of LCAs, KLCA 2 Rural and Urban Peripheral Village Landscape and KLCA-5 Lowland Agricultural Landscape are both predicted to experience insignificant impacts during construction and operation due to the limited influence such small works areas would have on the wider LCAs.
Mitigation measures in terms of limiting impacts on existing vegetation and topography have been recommended as best practice measures to ensure a high quality development for both LRs and LCAs where insignificant impact have been identified.
12B.10.1 Conclusion
Due to the very small construction footprint and relative low sensitivity of the LRs and LCAs affected by this DP, it is considered that all potentially adverse landscape impacts can be controlled through the implementation of construction and operational mitigation measures. The most effective measures in both locations arise from minimisation of the construction footprint in order to avoid impacting LRs unnecessarily combined with the provision of tree protection and compensatory planting, which can reduce all impacts to insignificant during the construction and operation stage.
In this case it is considered that the SPS within DP Package B would be acceptable in terms of landscape impacts.
Visual impacts have been assessed for the construction and
operational phases of the Schedule 2 DPs areas; the methodology is set out in Section 12.19.
12B.11.1
Visual
Baseline Conditions
The area covered by KTN NDA, of which the schedule 2 DP form part, is around 450 ha and is bound by the Closed Area Boundary to the north; Shek Sheung River to the east; Fanling Highway and Castle Peak Road to the south; and Pak Shek Au and Tit Hang villages to the west. The landscape character of the area can be broadly described as a low value, rural lowland area predominantly used for open storage and industrial uses, surrounded by higher value, natural landscape features, villages and interspersed agricultural land.
This locality is fairly enclosed by prominent green hill ranges in close proximity on three sides: the ridges of Tai Shek Mo to the north; Lok Ma Chau range to the west (Western ranges); and Ki Lun Shan and Ki Lun Shan Au to the south. The lower lying Ma Tso Lung valley runs between Lok Ma Chau range and Tai Shek Mo while between Lok Ma Chau range and Ki Lun Shan there is lower land containing Pak Shek Au village and the Fanling Highway. To the east of the land is generally flatter and more open until past the urban area of Sheung Shui, where the hill range including Cham Shan and Wa Shan is visible. Fung Kong Shan is also a prominent hill in the middle providing strong green backdrop. Hill slopes are undisturbed and mainly vegetated by grass and scrub vegetation with trees found principally in the foothills and major valleys. Villages such as Kam Tsin and Ho Sheung Heung have been established at the base of the foothills with clusters of trees or woodland on the lower slopes.
The central southern and south eastern parts of this landscape are generally flat with the central southern part being more developed and the south eastern part made up of the predominantly agricultural Long Valley. The Long Valley is a significant rural feature of this area with high landscape value, made up of a mix of active and inactive agricultural land, some ponds, small areas of marsh and mitigation wetlands with limited built structures. The central southern part of the study area is more developed, made up of mixed land uses such as small residential developments, scattered villages, agricultural lands, rural areas and rural industries including vehicle repair, construction material storage and container storage. Villages, such as Yin Kong Village and Ho Sheung Heung are generally made up of traditional houses with no high rise structures, complementing the rural surroundings. Rivers and streams are also important features of the local landscape. The channelised Sheung Yue River and Shek Sheung River are both dominant visual components of the landscape, made more conspicuous by their engineered embankments.
DP5 – New Sewage Pumping Stations (SPS) in KTN NDA.
Two SPS are proposed in KTN NDA to convey the sewage flows from KTN NDA to Shek Wu Hui Sewage Treatment Works for treatment and its disposal, details on their operational requirements are presented in Section 2.4.2.5. The SPS south of Ma Tso Lung sits within a predominantly undeveloped valley landscape formed by the hillsides of the Western Ranges and Fung Kong Shan. The surrounding landscape is used for agricultural purposes with small pockets of woodland and village developments. Long distance views are available to the south over the NDA area towards Lam Tsuen Country Park. Locally the landscape is level which, in combination with surrounding tree/ vegetation cover, restricts views at ground level to medium and short distances.
A second SPS south of Ho Sheung Heung is positioned close to Sheung Yue River within an agricultural landscape setting. Locally the landscape is well wooded and appears relatively natural, this is contrasted against the highly engineered appearance of the Sheung Yue River Channel which has been realigned and channelised. At ground level views are limited by the surrounding tree cover.
12B.11.2
Visual
envelope
The visual envelope (VE) for these DPs is generally shared with that of the KTN NDA project. Generally the viewshed is confined to the north and east by the ridgeline formed by the summits of Cheung Po Tau, Cham Shan, Wa Shan and reaching across to the more distant and easterly Tsung Shan and Mau Tau Leng summits. To the south east the foothills of Lung Shan contain the view while to the southern and western side the VE is contained by the high-rise development of Fanling / Sheung Shui with the mountain range of Tai Shek Mo in the background. The predominantly level landscape means than views from elevated positions can generally see very long distances whereas many ground level views are limited by intervening vegetation cover and built form.
Table 12B.11.1 below details the VPs in relation to DP 5 and describes their overall sensitivity. This information is also presented on the following figures: Figures 12.53.1 Vantage Point (VP) locations for DP 5.
Figures 12.53.11, 12 and 15 present existing views taken from vantage points within the study area looking towards the relevant NDA and the DPs. Representative photographs have been selected that present a typical view from the VSR relating to the DP. Since access could not be gained for all VSRs, especially for private residential developments, the representative viewing locations may have been adjusted if necessary, as described in the methodology. Bearing in mind most VSRs will have various views, and considering access was not always available, the selected photographs are considered the best alternative that represents the typical view of the VSRs.
Figures 12.55.4a, 4b, 7a and 7b provide representative photomontages showing the predicted view from selected viewpoints depicting existing conditions, Day 1 of Operation Phase without Mitigation Measures, Day 1 of Operation Phase with Mitigation Measures and Year 10 of Operation Phase with Mitigation Measures.
Table 12B.11.1 – VSRs and their sensitivity (DP 5)
VP CODE |
Name |
Category of VSR (Strategic/ District/ Local) |
Type of VSR |
Approximate Closest Viewing Distance (m) to Proposed Schedule 2 DP |
Number of Individuals (Very Many / Many / Few / Very Few) |
Quality of Existing View (Good / Fair / Poor) |
Availability of Alternative Views (Yes / No) |
Degree of Visibility (Full / Partial / Glimpse) |
Duration of view (Long, Medium, Short) |
Frequency of View (Very Frequent / Frequent / Occasional / Rare) |
Sensitivity (Low, Medium,
High) |
|||||||
Description of Existing View, particularly toward the Proposed DP |
||||||||||||||||||
KVP8 |
Ying Kong Village |
Local |
Residential – Low Rise |
275 |
Many |
Fair |
Yes |
Partial |
Long |
Frequent |
High |
|||||||
Views from edge of agricultural plots fronting Ying
Kong Village provide low level views across open and well managed farmland;
this is crossed by numerous telegraph poles and intermittent agricultural
buildings which detract from the quality of the views. The dense and uniform screening provided by
mature tree planting in the middle ground restricts long distance view
however the peaks and ridgeline of mountains in the distance appear above the
tree cover, such as the varied and steep terrain of Tai Shek Mo. The DP (SPS South of Ho Sheung Heung) would appear in the middle ground of the view
sitting within an existing tree belt. |
||||||||||||||||||
KVP9 (K6b) |
Ho Sheung Heung |
Local |
Residential - Low Rise |
100 |
Many |
Good |
No |
Glimpse |
Long |
Frequent |
High |
|||||||
Residential view from the
southern portion of Ho Sheung Heung looking south west over large area of
surface parking on un-made ground and broken areas of vegetation. These activities have degraded the quality of
the view in the foreground however; better quality long distance views are
possible to the hillside of Ki Lun Shan beyond the Long Valley. The nature of the view is very open and
apart from the car parking in the foreground, the landscape appears relatively
undeveloped in terms of built form.
The DP (SPS South of Ho Sheung Heung) would appear in the middle
ground beyond the existing un-surfaced car parking areas within an existing
tree belt. |
||||||||||||||||||
KVP12 |
Ma Tso Lung Shun Yee San Tsuen Village |
Local |
Residential – Low Rise |
300 |
Few |
Good |
Yes |
Partial |
Long |
Frequent |
High |
|||||||
This view is taken from midway long the access road running
past the village at an opening overlooking the adjacent agricultural
land. The landscape to the south of
the village is generally level which allows long distance views towards the
mountains and ridgelines within Lam Tsuen Country Park. Pockets of woodland planting throughout
this lowland area conceal other development and enhance a strong rural
character. The DP (SPS South of Ma Tso
Lung) would appear in the middle ground of the view across the open field in
the foreground just beyond several isolated tree clumps. |
||||||||||||||||||
Remarks: The approximate closest viewing distance to the proposed schedule 2 DP is measured from the edge of the VSR group to the closest built form proposed within the DP.
The potential sources of visual impact due to the Project are described in Section 12B.4 & 5. They will create varying levels of visual impact during the construction and operation phases in relation to the DP, due to factors such as obstruction of views, degradation of the visual quality of existing views and visual incompatibility with the surrounding visual context.
The magnitude of visual change is largely dependent on a number of factors as outlined in the methodology. In general, the magnitude of change will reduce the further a VSR is from the Project.
Detailed engineering design of built elements in the NDA is on-going at this stage therefore, the structures shown in the photomontages may change as detailed design is refined.
Table 12B.12.1 details the magnitude of change in relation to DP 5.
Table 12B.12.1 - Magnitude of visual
change for VSRs due to Schedule 2 DP5
in
KTN NDA
Remarks: The approximate closest viewing distance to the
proposed NDA is measured from the edge of the VSR group to the closest
built structure proposed within the DP.
VSR Code |
Name |
VSR Category (Strategic/ District/ Local) |
Key Designated Projects (DPs)/ Sites with Structures causing Visual
Impact (Land Use Type)* |
Blockage of View (Full/ Partial/ Nil) |
Approximate Closest Viewing Distance to Proposed NDA (m) |
Scale of Development (Large/ Medium/ Small) |
Compatibility with Surrounding Landscape |
Duration of Impact |
Reversibility of Change |
Magnitude of Change (Large/ Intermediate/ Small/ Negligible) |
||||||
Construction |
Operation |
Construction |
Operation |
Construction |
Operation |
Construction |
Operation |
|||||||||
Description of Impacts during Construction and Operation |
||||||||||||||||
|
KVP8 |
Ying Kong Tsuen Village |
Local |
DP5 SPS South of Ho
Sheung Heung |
Nil |
275 |
Small |
Fair |
Fair |
Temporary [Medium] |
Permanent |
Reversible |
Irreversible |
Small |
Small |
|
|
|
Description of Key Impacts during Construction and Operation Vegetation clearance within the footprint of the site will be visible
during the construction period however, due to the elevation of this view it
is unlikely that views of any ground works would be possible. In operation it is predicted that the south
eastern elevation of the SPS and associated perimeter wall would be partly
visible through the trees. As a result of the small scale nature of the development, it is
considered that the compatibility of the work in construction and operation
would be fair. In the future the NDA
development would for the backdrop to the SPS which would further enhance its
compatibility. Due to the limited size of the proposed built form and the wide angle
of the views across this open landscape, the magnitude of change during
construction would be small, as
the built form is likely to remain partly visible from this point during
operation the magnitude of change would remain small. |
||||||||||||||
Y |
KVP9 (K6b) |
Ho Sheung Heung |
Local |
DP5 SPS South of Ho
Sheung Heung |
Partial |
100 |
Small |
Fair |
Fair |
Temporary [Medium] |
Permanent |
Reversible |
Irreversible |
Small |
Negligible |
|
|
|
Description of Key Impacts during Construction and Operation Vegetation clearance within the footprint of the site will be visible
during the construction period however, due to the elevation of this view it
is unlikely that views of any ground works would be possible. In operation it is predicted that the north
tip of the roof structure would be visible over the top of the low vegetation
in the intervening ground in the view. As a result of the small scale nature of the development, it is
considered that the compatibility of the work in construction and operation would
be fair. In the future the SPS would
be fully integrated into the surrounding NDA development which would further
enhance its compatibility. Due to the limited extent of the building that would be visible and
the disturbed nature of the landscape in the foreground, the magnitude of
change during construction would be small,
reducing to negligible during
operation. |
||||||||||||||
Y |
KVP12 |
Ma Tso Lung Shun Yee San Tsuen Village |
Local |
DP5 SPS South of Ma Tso Lung |
Partial |
300 |
Small |
Poor |
Fair |
Temporary [Short] |
Permanent |
Reversible |
Irreversible |
Small |
Small |
|
|
|
Description of Key Impacts during Construction and Operation Vegetation clearance and ground works are likely to be visible during
the construction period in the middle ground of the view however, due to the
sloping topography; lower level views of the development may be
concealed. In operation it is
predicted that the northern elevation of the perimeter wall would be visible
including the internal SPS building roof structure. Initially the development would appear in an area which undeveloped
and rural in appearance, in this regard it is considered that the development
would have a poor compatibility during construction. The KTN NDA development will form an urban
backdrop in the future; in this case the compatibility is likely to be fair. Due to the limited size of the building and the broad panoramic nature
of the views across this open landscape, the magnitude of change during
construction would be small, as
the built form is likely to remain partly visible from this point during
operation the magnitude of change would remain small. |
||||||||||||||
Based on the sensitivity assessment of VSRs as described in Section 12B.11 and the magnitude of change they might experience described in Section 12B.12 the potential significance of the unmitigated visual impacts from DPs during the construction and operation are provided in Table 12B.13.1 using the matrix given in the methodology, and taking into account site visits to the area.
Residual impact significance is also determined in this Section, considering the mitigation measures described in full in Section 12B.9.
Figures 12.55.4a, 4b, 7a and 7b provide representative photomontages showing the predicted view from selected viewpoints depicting existing conditions, Day 1 of Operation Phase without Mitigation Measures, Day 1 of Operation Phase with Mitigation Measures and Year 10 of Operation Phase with Mitigation Measures.
Table 12B.13.1 - Significance of Visual
Impacts for DP5
VSR Code |
Name |
VSR Category (Strategic/ District/ Local) |
VSR Type |
VSR Sensitivity (High/ Medium/ Low) |
Magnitude of Change (Large/ Intermediate/ Small/ Negligible) |
Impact Significance BEFORE Mitigation (Substantial/ Moderate/ Slight/
Insignificant) |
Recommended Mitigation Measures |
Residual Impact Significance UPON Mitigation (Substantial/ Moderate/
Slight/ Insignificant) |
|||||
Construction |
Operation |
Construction |
Operation |
Construction |
Operation |
Construction |
Operation
Day 1 |
Operation
Year 10 |
|||||
KVP8 |
Ying Kong Village |
Local |
Residential - Low Rise |
High |
Small |
Small |
Moderate |
Moderate |
2, 4, 11,16, 17 |
9, 10, 11, 12, 17 |
Slight |
Slight |
Insignificant |
KVP9 (K6b) |
Ho Sheung Heung |
Local |
Residential - Low Rise |
High |
Small |
Negligible |
Moderate |
Negligible |
2, 4, 11, 16, 17 |
9, 10, 11, 12, 17 |
Slight |
Insignificant |
Insignificant |
KVP12 |
Ma Tso Lung Shun Yee San Tsuen Village |
Local |
Residential - Low Rise |
High |
Small |
Small |
Moderate |
Moderate |
2, 7, 9, 10, 11,
16, 17 |
7, 9, 10, 11, 16,
17 |
Slight |
Slight |
Insignificant |
VSRs in very close proximity with more entire views will experience slightly more prolonged impacts as development works will occupy a greater proportion of the view and screening works / visual mitigation will require an establishment period before they take full effect.
VSRs in the vicinity of KVP 8 Ying Kong Village and KVP 9 Ho Sheung Heung and KVP 12 Ma Tso Lung Shun Yee San Tsuen Village would all experience moderate adverse visual impacts prior to mitigation in relation to the development during the construction stage, given that these are close hand views and the high sensitivity of these residential type VSRs. Screen hoarding works around the perimeter of the works area and light control during construction will assist in reducing visual impact together with protection and preservation of existing tree cover where possible. Measures to enhance the visual quality of the architectural form, textures, finishes and colours of the proposed SPS buildings and boundary treatment are considered to be effective in the visual integration of the buildings into the existing and future landscape setting especially during the construction and early operational stages. The treatment of the SPS facades and boundary should also reflect the materials and architectural styles of the surrounding proposed development in order to maximise visual integration. Vertical greening around the perimeter walling will also help to break up the uniform surfaces. A green roof will help to reduce the visibility of roofscape from elevated viewpoints. Compensation / screen planting will also be required around the perimeter of the buildings to break up the visibility of structures.
Due to the small extent of structure that would be visible from KVP9, the impact would reduce to insignificant at operation day 1 as the visual impact would principally be associated with the construction operations.
As elevations of the proposed structures will remain partially visible from KVP 8 and 12, slight adverse impacts will remain at operation day 1. These will reduce to insignificant by operation year 10 when screen planting and vertical greening will have taken full effect.
In the case of DP Package B, it is considered the potential visual impacts would be acceptable.
12B.14.1
Landscape
Character Areas
In summary for the LCAs, KLCA 2 Rural and Urban Peripheral Village Landscape and KLCA-5 Lowland Agricultural Landscape are both predicted to experience insignificant impacts during construction and operation due to the limited influence such small works areas would have on the wider LCAs. In both cases it is considered that through landscape mitigation measures that these structures can quickly be assimilated into the landscape and there would be no significant adverse residual impacts.
Mitigation measures in terms of limiting impacts on existing vegetation and topography have been recommended as best practice measures to ensure a high quality development for both LRs and LCAs which insignificant impact have been identified.
12B.14.2
Landscape
Resources
In summary, KLR 1.3 Sheung Yue River is predicted to experience slight adverse impacts prior to mitigation. It is considered that mitigation measures proposed which consist of minimising topographical change and enhancement planting along the embankment of Sheung Yue River, the significance of impact will reduce to insignificant in the construction and operation stage.
KLR 8.3 Shrubland/Grassland Mosaic in Tai Shek Mo and the Western Range Foothills is predicted to experience slight adverse impacts during construction, prior to mitigation. It is considered that mitigation measures proposed which consist of preserving and protecting trees where possible, transplanting trees which cannot be retained insitu and compensating plating directly around the SPS will reduce this impact to insignificant in the construction and operational stage.
KLR 9.3 Agricultural Lands in Shek Tsai Leng, Tong Kok and Fung Kong is also predicted to experience slight adverse impacts during construction, prior to mitigation. It is considered that mitigation measures proposed which consist of preserving and protecting trees where possible, transplanting trees which cannot be retained insitu and compensating plating directly around the SPS will reduce this impact to insignificant in the construction and operational stage.
All other LR would experience insignificant impacts during construction and operation.
12B.14.3
Visual
Impact
The significant visual impacts due to each SPS are provided below together with a description of the effectiveness of the recommended mitigation measures.
VSRs in very close proximity with more entire views will experience slightly more prolonged impacts as development works will occupy a greater proportion of the view and screening works / visual mitigation will require an establishment period before they take full effect.
VSRs in the vicinity of KVP 8 Ying Kong Village and KVP 9 Ho Sheung Heung and KVP 12 Ma Tso Lung Shun Yee San Tsuen Village would all experience moderate adverse visual impacts prior to mitigation in relation to the development during the construction stage, given that these are close hand views and the high sensitivity of these residential type VSRs. Screen hoarding works around the perimeter of the works area together with light control during construction will assist in reducing visual impact together with protection and preservation of existing tree cover where possible. Measures to enhance the visual quality of the architectural form, textures, finishes and colours of the proposed SPS buildings and boundary treatment are considered to be effective in the visual integration of the buildings into the existing and future landscape setting. The treatment of the SPS facades and boundary should also reflect the materials and architectural styles of the surrounding proposed development in order to maximise visual integration. Vertical greening around the perimeter walling will also help to break up the uniform surfaces. A green roof will help to reduce the visibility of roofscape from elevated viewpoints. Compensation / screen planting will also be required around the perimeter of the buildings to break up the visibility of structures.
Due to the small extent of structure that would be visible from KVP9, the impact would reduce to insignificant at operation day 1 as the visual impact would principally be associated with the construction operations.
As elevations of the proposed structures will remain partially visible from KVP 8 and 12, slight adverse impacts will remain at operation day 1. These will reduce to insignificant by operation year 10 when screen planting and vertical greening will have taken full effect.
12B.14.4
Cumulative impacts
12B.14.5
KTN NDA
The assessment of impacts in relation to LRs and LCAs in this section has considered the construction of the Schedule 2 DPs in isolation so that it is possible to identify and quantify their specific influences and contributions to potential landscape and visual impacts within the wider NDA project. In general the construction footprint of the Schedule 2 DPs are significantly smaller than the Schedule 3 components and the associated impacts on LRs and LCAs are also far smaller. When considered together the impact of the Schedule 2 projects would not alter the outcome of the Schedule 3 assessment as this has taken into the account the same LRs/LCAs within broadly the same study area.
In terms of visual impact, the majority of the DPs will be integrated directly within or around the KTN NDA therefore in operation, they will be entirely screened from external views and would not generate any adverse visual impacts.
12B.14.6
Agreement
No. CE38/2010(CE) Planning Study
on Liantang/Heung Yuen Wai Cross-boundary Control Point and its Associated
Connecting Roads in Hong Kong – Feasibility Study.
A new Boundary Control Point (
12B.14.7
Agreement
No. CE53/2008(CE) Planning and Engineering Study on Development of Lok Ma Chau
Loop - Investigation
The LMC Loop eastern connection road lies within the study
area of KTN NDA; this will link to DP 4 (KTN NDA Road D1 to D5) distributor
road south of Ma Tso Lung. This road
would basically comprise a continuation of the DP4 works further to the
north. This project is remote from this
DP and therefore would not generate any additional impact.
12B.14.8
Widening
of Tolo Highway/ Fanling Highway between Island House Interchange and Fanling
(Stage 2)
This project will interface with DP1 Fanling Bypass Eastern section to the south east of Fanling. The tentative completion date of the project is from Yr 2015 to Yr 2018 but is still under review by HyD. This project is remote from this DP and therefore would not generate any additional impact.
12B.14.9
Construction
of cycle tracks and the associated supporting facilities from Sha Po Tsuen to
Shek Sheung River.
This project will interface with DP5 SPS south of Ho Heung Sheung however It is considered that these cycleway would be highly compatible with the DP works and that no significant negative impacts would be generated.
12B.14.10 Overall Conclusion
Due to the very small construction footprint and relative low sensitivity of the LRs and LCAs affected and limited number of associated VSRs of this DP, it is considered that potentially adverse landscape and visual impacts can be controlled through the implementation of construction and operational mitigation measures. The most effective measures in both locations arise from consideration of the architectural details and choice of materials, at the detailed design stage, so that the buildings would complement the future urban environment. Screen planting would be integrated into the proposed amenity planting within the surrounding landscape areas, also compensating for any tree losses during the construction stage. Vertical greening measures and application of green roofs will assist with visual integration during the early operational stages, to help break up the appearance and uniformity of roofscape, building facades and boundary treatments.
In this case it is considered that the SPS within DP 5 would be acceptable in terms of landscape and visual impacts.