TABLE OF CONTENTS
Project Background
Objectives of the Environmental Impact
Assessment
Description of the Project
Air Quality
Noise
Water Quality
Waste Management Implications
Landscape and Visual Impact
Cultural Heritage
3 Environmental
Monitoring and Audit
List of
Figures
Figure 1.1 Location
of Proposed Tuen Mun Area 54 Sewage Pumping Station
1.1
According
to the Territorial Development Strategy Review in 1996, the housing supply
capacity of approved plans and programmes would not be adequate to meet the
estimated housing demand after 2001. In response to the estimated shortfall in
flat supply, the Government identified a list of areas, including Tuen Mun Area
54, having potential for housing development.
1.2
The
New Territories West Development Office (NTWDevO) of Territory Development Department
(TDD) completed the “Planning and Development Study of Potential Housing Site
in Area 54, Tuen Mun” (the Study) in 1999 under Agreement No. CE21/97. The
Study put forward proposals on housing types, development parameters and
planning layouts and assessed the development impacts on transport network,
infrastructural capacities and environmental quality.
1.3
In
order to convey the sewage collected from Tuen Mun Area 54 to the existing
sewers at Ming Kum Road, a new sewage pumping station, close to Tsz Tin Road,
will be constructed and operated, with a capacity of about
Objectives of the Environmental Impact Assessment
1.4
The
proposed TM54SPS is classified as a Designated Project under Schedule 2, Part
I, F3(b) of the Environmental Impact Assessment Ordinance (EIAO), i.e. a sewage
pumping station with an installed capacity of more than
1.5
The
EIA study has been undertaken to provide information on the nature and extent
of environmental impacts arising from the construction and operation of the
Project and all related activities taking place concurrently.
1.6
This
Executive Summary provides a summary of the key findings of the EIA study,
including an assessment of potential air quality, noise, water quality, waste,
cultural heritage, visual and landscape impacts from the construction and operation
phases of the Project, and recommendations for mitigation measures to comply
with environmental legislations and standards.
1.7
The
proposed TM54SPS is located in the central part of Site
1.8
According to the Review of Tuen
Mun and Tsing Yi Sewerage Master Plans, the TM54SPS will receive sewage from
the proposed development in Area 54, the four recognized villages within Area
54 namely Tsz Tin Tsuen, Po Tong Ha, Kei Lun Wai and Siu Hang Tsuen, and the
proposed Tuen Mun North Sewage Pumping Station in Area 52.
1.9
The
proposed TM54SPS is required to convey the sewage collected from Tuen Mun Area
54 to the existing trunk sewers at
1.10
The
construction works for the Project are scheduled to commence in early 2011 for
completion in early 2014.
2.1
The
following sections summarize the environmental impacts and outcomes arising
from the construction and operation of the Project and the recommended
mitigation measures.
2.2
In
view of limited work site area, low amount of excavated soil generated during
construction and the existing nearby air sensitive receivers (ASRs) located far
away from the site, insignificant construction dust impact at the existing ASRs
in the vicinity of the work site is expected with adoption of dust suppression
measures stipulated in Air Pollution
(Construction Dust) Regulation and good site practices. There would have two other projects to be
undertaken concurrently within
2.3
During
operational phase, major air quality impact would be related to the potential
odour emission from the TM54SPS.
The odour sources, namely wet wells and screening chambers, would be enclosed
and the vented air would be treated in the deodourizing unit with 90% odour
removal efficiency, before discharging into the atmosphere. The computer dispersion model results
showed that the predicted odour levels at the nearest ASRs around the TM54SPS
would be below the EPD odour criteria of 5 ou over 5-second average. Adverse residual odour impact would not
be expected. A standby deodourizing
unit (90% odour removal efficiency) would be provided to cater for breakdown
and maintenance of the duty deodourizer.
2.4
Potential
noise impact arising from the construction of the TM54SPS at the noise
sensitive receivers (NSRs) in the vicinity of the construction site was
assessed. With the adoption of
quieter plant, the predicted construction noise levels at the NSRs N1 and N2
would comply with the construction noise criteria stipulated in Technical
Memorandum on Environmental Impact Assessment Process (EIAO-TM). Good site practices were also proposed
to further abate the impacts on the NSRs.
As mentioned in Section 2.2, there are two other projects to be
undertaken concurrently. The
village sewerage works at Kei Lun Wai and Unicorn Garden (within 300m of the
study area) would be scheduled to prevent overlapping with the construction of
TM54SPS, the cumulative noise impact from site formation and superstructure
works at Site 2 was only considered in the cumulative construction noise impact
assessment. Results indicated that
the cumulative construction noise levels at representative NSRs would comply
with EIAO-TM construction noise criteria.
2.5
During
the operational phase, the transformer is housed in enclosed reinforced
concrete structure with soundproof door.
The pumps and mechanically raked screens are also housed in reinforced concrete
structure with soundproof door and acoustic silencers would be provided for the
louvers of the pump house. Silencer
would also be provided for the exhaust fan of deodorization unit. The predicted operational noise levels
at all NSRs would comply with the daytime, evening time and nighttime noise
criteria. Adverse residual
operational noise impacts would not be expected.
2.6
Water
quality impacts from construction of the TM54SPS can be controlled to
acceptable levels by implementing the recommended mitigation measures. All the effluents and sediment-laden
runoff generated from the works area shall be treated and their quality should
be monitored before discharge. No
acceptable water quality impacts would be expected from the land-based
construction activities. Site
inspections should be undertaken routinely to inspect the works area in order
to ensure the recommended mitigation measures are properly implemented.
2.7
With
the incorporation of all the proposed precautionary measures in the design of
the sewage pumping station, minimal residual operational water quality impact
is expected.
2.8
Waste
generated by the construction activities are likely to include C&D
materials from the construction works, general refuse from workforce, chemical
waste from construction plant and equipment. Provided that these identified waste
arising are handled, transported and disposed of using approved methods and that
the recommended good site practices are strictly followed, adverse
environmental impacts are not expected during the construction phase.
2.9
There
are no tree would be affected within the site boundary.
2.10 The landscape resources of Farmland / Orchard (LR1) and landscape character area of Farmland Landscape Character Area (LCA2) will be moderate impact by the construction of an incongruous building mass, temporary works areas, additional construction traffic, storage of construction material and general loss of farmland plantation. After the implementation of mitigation measure both LR1 and LCA2 landscape Impact will be lessen as sight as additional tree will be planted along the boundary of the proposed pumping station for screening and possible loss of greenery.
2.11
Residents in existing villages
of
2.12
After
the proposed mitigation measures have been implemented, the proposed heavy standard sized tree planting would carry out ultimate screening,
all residual adverse
landscape and visual impacts in operational phase will be insubstantial
significance. Except on
2.13
As
the site of the proposed TM54SPS falls within the boundary of the Kei Lun Wai
Archaeological Site, construction of the proposed TM54SPS would likely have direct
impact on the archeological resources within the archaeological site. It is recommended that Site 4A of Tuen
Mun Area 54 be added to the programme of archaeological survey and rescue
excavation to be undertaken by the Antiquities and Monuments Office (AMO) of
Leisure and Cultural Services Department (LCSD) for the proposed development at
Tuen Mun Area 54 prior to the commencement of construction works. As the archaeological survey cannot be
conducted in this EIA stage due to land access constraint, the proposed works
area for the TM54SPS which is located within Site 4A would therefore be
assessed in the future archaeological survey and rescue excavation.
2.14
Since
there are no built heritage resources within the study area, impact on built
heritage resources is not expected.
3 Environmental Monitoring and Audit
3.1
Environmental
monitoring and audit are recommended for dust, odour and construction noise, to
check compliance with relevant statutory criteria and to ensure the effectiveness
of the mitigation measures. Site
inspection and audit are also recommended for water quality and waste
management during construction.
Details of the recommended mitigation measures, monitoring procedures
and locations are presented in a stand-alone Environmental Monitoring and Audit
(EM&A) Manual. This will enable
the Contractor to have early warning and provide necessary action to reduce
impacts at specific areas if the critical assessment criteria are
approached. The effectiveness of on-site
control measures would also be evaluated through a monitoring exercise. All the recommended mitigation measures
will be incorporated in an EM&A programme during implementation.
4.1
The
findings of this EIA Study have determined the likely nature and extent of
environmental impacts predicted to arise from the construction and operation
phases of the Project. The EIA has,
where appropriate, identified mitigation measures to ensure compliance with
environmental legislation and standards.
4.2
Overall,
the EIA Study for the proposed TM54SPS has predicted that the Project, with the
implementation of the proposed mitigation measures for construction and operation
phases, would comply with all applicable environmental standards and
legislation. This EIA has also
demonstrated the acceptability of the residual impacts from the Project and the
protection of the population and environmentally sensitive resources. Environmental monitoring and audit
mechanisms have been recommended to verify the effectiveness of recommended
mitigation measures.