12
Noise Impact.. 12-1
12.1 Introduction
12-1
12.2 Environmental Legislation, Standards and Criteria 12-1
12.3 Description Of Environment 12-4
12.4 Noise Sensitive Receivers 12-4
12.5 Assessment Methodology 12-4
12.6 Identification and Evaluation of Noise Impacts 12-5
12.7 Mitigation Measures 12-6
12.8 Environmental Monitoring and Audit Requirements 12-6
12.9 Conclusion
12-7
List
of TABLES
Table 12.1
EIAO-TM Day-time Construction Noise Standards. 12-1
Table
12.2 Area Sensitivity Ratings (ASRs). 12-2
Table 12.3
Acceptable Noise Levels (ANLs) for General Construction Works to be carried out
during Restricted Hours (GW-TM). 12-3
Table
12.4 Acceptable Noise Level for Fixed Plant Noise. 12-3
List
of figures
Figure 12.1
Noise Impact Assessment Boundary
12
Noise
Impact
12.1
Introduction
12.1.1
This Section provides an evaluation of the potential noise impacts
arising from the construction and operation of the proposed Project.
Appropriate mitigation measures have been recommended, where necessary, in
order to mitigate any unacceptable impacts.
12.2
Environmental Legislation, Standards and Criteria
Construction Phase
12.2.1
The principal legislation relating to the control of construction noise
of the Project is the Environmental Impact Assessment Ordinance (EIAO) (Cap.
499). The Technical Memorandum on Environmental Impact Assessment Process
(EIAO-TM), issued under the EIAO, provides guidelines and noise criteria for
evaluating noise impacts. The assessment criteria are defined in Annex 5 of the
EIAO-TM. The guidelines for noise assessment are provided in Annex 13 of the
EIAO-TM.
12.2.2
The Noise Control Ordinance (NCO) (Cap. 400) also provides means to
assess construction noise impacts. A number of Technical Memoranda (TMs)
have been issued under the NCO to stipulate control approaches and
criteria. The Technical Memorandum on Noise from Construction Work Other
than Percussive Piling (GW-TM) provides the guidelines for controlling the
construction noise from powered mechanical equipment (PME) in general
construction works during the restricted hours. The Technical Memorandum on
Noise from Construction Works in Designated Areas (DA-TM) provides the
guidelines for controlling the use of Specified Powered
Mechanical Equipment (SPME) and the undertaking of Prescribed
Construction Work (PCW) during the restricted hours in designated areas.
General
Construction Works during Normal Working Hours
12.2.3
Under the EIAO, potential noise impact arising from general construction
works during normal working hours (i.e. 0700 to 1900 hours on any day not being
a Sunday or general holiday) at 1 m from the external façade of the noise
sensitive uses, which rely on opened windows for ventilation, is to be assessed
in accordance with the noise criteria specified in the EIAO-TM. The EIAO-TM
noise standards are presented in Table 12.1.
Table
12.1 EIAO-TM Day-time
Construction Noise Standards
Noise
Sensitive Uses
|
0700 to 1900 hours on any day not being a Sunday or general holiday
Leq, 30 min (dB(A))
|
ĄP All domestics premises including temporary housing accommodation
|
75
|
ĄP Hotels and hostels
|
75
|
ĄP Educational Institutions including kindergartens, nurseries and all
others where unaided voice communication is required
|
70 (During normal periods)
65 (During examination periods)
|
Notes:
(1) The above standards apply to uses which rely on opened
windows for ventilation.
(2) The above standards shall be viewed as the maximum
permissible noise levels assessed at 1m from the external façade.
General Construction
Works during Restricted Hours
12.2.4
The NCO provides statutory controls on general construction works during
restricted hours (i.e. 1900 to 0700 hours or any time on Sundays or general
holidays). The use of PME for carrying out construction works during
these restricted hours would require a Construction Noise Permit (CNP).
The Noise Control Authority will assess all CNP applications on a case-by-case
basis and, in doing so the authority advises that they will be guided by the
GW-TM.
12.2.5
When assessing an application for CNP for the use of PME during
restricted hours, the Noise Control Authority will compare the Acceptable Noise
Levels (ANLs) specified in the GW-TM with the Corrected Noise Levels (CNLs)
(i.e. after accounting for factors such as barrier effects and reflections)
associated with the proposed PME operations. The NCO requires that noise
levels from construction at affected Noise Sensitive Receiver (NSR) be less
than the specified ANL. The ANLs are related to the inherent noise
sensitivity of the noise receiver areas in question. Different Area Sensitivity
Ratings (ASRs), i.e. A, B or C (see
Table 12.2), have been established to reflect the background
characteristics of different areas. Each noise receiver area is assigned
an ASR based on its predominant land use and the presence, if any, of
Influencing Factors (IFs) such as nearby industrial areas, major roads or
airports. The appropriate ASR for the NSR is determined with reference to
Table 12.2.
Table 12.2 Area Sensitivity Ratings (ASRs)
Type of Area Containing NSR
|
Degree to which
NSR is affected by Influencing Factor
|
Not Affected
|
Indirectly
Affected
|
Directly
Affected
|
Rural area, including country parks or
village type developments
|
A
|
B
|
B
|
Low density residential area consisting of
low-rise or isolated high-rise developments
|
A
|
B
|
C
|
Urban area
|
B
|
C
|
C
|
Area other than those above
|
B
|
B
|
C
|
Notes:
The
following definitions apply:
(a)
"Country Park" means an area
that is designated as a country park pursuant to section 14 of the Country
Parks Ordinance;
(b)
"directly affected" means that
the NSR is at such a location that noise generated by the IF is readily
noticeable at the NSR and is a dominant feature of the noise climate of the
NSR;
(c)
"indirectly affected" means
that the NSR is at such a location that noise generated by the IF, whilst
noticeable at the NSR, is not a dominant feature of the noise climate of the
NSR;
(d)
"not affected" means that the
NSR is at such a location that noise generated by the IF is not noticeable at
the NSR; and
(e) "urban area" means an area
of high density, diverse development including a mixture of such elements as
industrial activities, major trade or commercial activities and residential
premises.
12.2.6
The relevant ANLs for each ASR are shown in Table 12.3.
Table 12.3 Acceptable Noise Levels (ANLs) for
General Construction Works to be carried out during Restricted Hours (GW-TM)
Time period
|
Area Sensitivity Rating
Leq,
5 min (dB(A))
|
|
A
|
B
|
C
|
All days during the evening (i.e. 1900-2300 hrs) and general holidays
(including Sundays) during the day and evening (i.e. 0700-2300 hrs)
|
60
|
65
|
70
|
All days during the night-time (i.e. 2300-0700 hrs)
|
45
|
50
|
55
|
Note:
(1) The above standard applies to uses which rely on opened windows
for ventilation.
|
12.2.7
The Noise Control Authority will consider a well-justified CNP
application for construction works within restricted hours as guided by the
relevant Technical Memorandum issued under the NCO. The Noise Control
Authority will take into account adjoining land uses and any previous
complaints against construction activities at the site before making a
decision. Factors influencing the outcome of a CNP application, such as
the assigning of ANLs, would be determined by the Noise Control Authority at
the time of the application review based on the prevailing site conditions which
may change from time to time.
Percussive Piling
12.2.8
Percussive piling is prohibited between 1900 and 0700 hours on any days not
being a general holiday and at any time on Sunday or general holiday. A
CNP is required for the carrying out of percussive piling between 0700 and 1900
hours on any day not being a general holiday. Technical Memorandum on
Noise from Percussive Piling (PP-TM) sets out the requirements for working and
determination of the permitted hours of operations for the CNP
applications. The permitted hours of operations would be 3, 5 or 12 hours
per day depending on the types of percussive piling and the predicted noise
impact at NSRs.
Operational Phase
12.2.9
Fixed plant noise associated with the operation of a project is
controlled under Section 13 of the NCO, and the Technical Memorandum for the
Assessment of Noise from Places Other than Domestic Premises, Public Places or
Construction Sites (IND-TM).
12.2.10 The
noise criteria, in terms of ANLs, stipulated in the IND-TM apply for all days
and general holidays. The ANLs are dependent on the ASR of the NSRs and
the time of the day and are presented in Table 12.4.
Table 12.4 Acceptable Noise Level for Fixed
Plant Noise
Time Period
|
ANL Leq
30-min, dB(A)
|
ASR A
|
ASR B
|
ASR C
|
Day (0700 to 1900 hours)
|
60
|
65
|
70
|
Evening (1900 to 2300 hours)
|
60
|
65
|
70
|
Night (2300 to 0700 hours)
|
50
|
55
|
60
|
12.2.11 In any event, the above Area Sensitivity
Ratings are for indicative assessment only. It should be noted that the
fixed noise sources are controlled under Section 13 of the NCO. At the time of
investigation, the Noise Control Authority shall determine the noise impact
from the concerned fixed noise sources on the basis of prevailing legislation
and practices being in force, and taking into account the existing adjoining
land uses. Nothing in the EIA Report shall bind the Noise Control
Authority in the context of law enforcement against all the fixed noise sources
being assessed.
12.2.12 The
EIAO-TM recommends that the level of the intruding noise at the façade of the
nearest sensitive use should be at least 5 dB(A) below the appropriate ANL
or, in the case of background noise being 5 dB(A) lower than the ANL, the
predicted noise level arising from the operation of the proposed Project at the
façade of the nearest sensitive use should not exceed the background noise
level. The closest NSRs are village type developments located to the north
and northeast of Tai Po Industrial Estate (TPIE) outside 500m from the Project
site. It is not necessary to assign the Area Sensitive Rating for these NSRs.
12.3
Description of Environment
12.3.1
The existing Tai Po Sewage Treatment Works (TPSTW) and the proposed
expansion site are located at the south-eastern side of TPIE as shown in Figure 12.1. To the east of the
Project site is Shuen Wan Restored Landfill, whereas the south, west and north
are industrial buildings. The prevailing noise climate of assessment area is
dominated by the local traffic and industrial activities within Tai Po
Industrial Estate.
12.4
Noise Sensitive Receivers
12.4.1
Representative noise sensitive receivers (NSRs) were identified
according to the criteria set out in the EIAO-TM. The assessment area for noise
impact assessment area for noise impact assessment is defined by a distance of
300m from the Project boundary as specified in the Environmental Impact
Assessment (EIA) Study Brief. The assessment boundary is shown in Figure 12.1.
12.4.2
The 300 m study area is within the Tai Po Outline Zoning Plan (OZP) No.
S/TP/30. The relevant OZP, Development Permission area Plans, Outline
Development Plans and Layout Plans published by Lands Department and the land
use and development applications approved by the Town Planning Board have been
reviewed. Site survey has also been conducted for identifying NSRs.
12.4.3
Based on the review and site visit, no existing, committed or planned
NSR was identified within 300m from the boundary of the Project Area and works
of the Project. The staff quarters of TPSTW as identified in approved EIA
Report for TPSTW Stage V (Register No. AEIAR-081/2004) is no longer in use as
confirmed by the Drainage Services Department (DSD). The planned residential
development at Ting Kok, which is located over 500m away to the north-east of
the Project site, is identified as the nearest representative NSR as shown in Figure 12.1. Other NSRs such as
Casa Brava to the north and Fortune Garden to the east do not have direct line
of sight to the Project site (as they are blocked by existing buildings or
topography).
12.5
Assessment Methodology
12.5.1
Since no existing, committed and planned NSR was identified within 300m
from the boundary of this Project, quantitative noise assessments for the
construction and operation of the proposed Project are considered not
necessary. Qualitative assessment on construction noise and fixed noise sources
impact assessments have been conducted for the Project.
Construction Phase
12.6.1 Potential source of noise impact during
construction phase of the Project would be the use of PME for various
construction activities. Major construction works of the Project would include
demolition of existing facilities of TPSTW, foundation and superstructure works
for the upgraded TPSTW. The construction of this Project is tentatively
scheduled to commence in mid-2025 for completion in 2036. Since no NSR
was identified within the 300m assessment area of this Project, no unacceptable
construction noise impact would be expected due to this Project. Percussive
piling and general construction works using power mechanical equipment during
restricted hours are not required for the construction of the Project.
12.6.2 Relevant projects near
the Project site are the Shuen Wan Golf Course (EIAO Register No.
AEIAR-221/2019), the Tolo Harbour Effluent Export Scheme (THEES) upgrading
proposed under Ą§Agreement No. CE 13/2015 (DS)Ą¨ and the Development of Organic
Waste Pre-treatment Centre (New Territories East) proposed under Ą§Agreement No.
CE 5/2021 (EP)Ą¨.
12.6.3 The proposed Shuen Wan Golf Course (SWGC)
mainly involves the development of an 18-hole golf course within the existing
Shuen Wan Restored Landfill (SWRL) to the east of the Project site. Location of
the SWRL is shown in Figure 12.1.
The construction of the proposed SWGC is scheduled for completion by 2023 and
therefore would not contribute any cumulative construction noise impact with
this Project.
12.6.4 The proposed THEES
upgrading works involve the expansion of the Tai Po Effluent Pumping Station
(TPEPS) within the existing TPSTW site, installation of a new submarine
pipeline (across the inner Tolo Harbour) by the Horizontal Directional Drilling
(HDD) method and laying of a new effluent rising mains (connecting the new
TPEPS to the new submarine pipeline). The proposed Organic Waste Pre-treatment
Centre (OWPC) involves the re-development of the existing Shuen Wan Leachate
Pre-treatment Works and the existing pilot-scale Food Waste Pre-treatment
Facilities to the north of the existing TPSTW site into a full-scale OWPC.
Locations of the proposed THEES upgrading and OWPC are shown in Figure 12.1.
12.6.5 Based on the best available information, the tentative
construction period for the proposed THEES upgrading and the proposed OWPC are
2025-2031 and 2025-2029 respectively. The construction works limits for the
proposed THEES upgrading and the planned OWPC would be located over 500m from
the closest representative NSR of this Project (i.e. the planned residential
development at Ting Kok). Due to the large buffer distance, no unacceptable
cumulative construction noise impact would arise from the concurrent projects.
Operational
Phase
12.6.6 Potential fixed plants noise would be
generated from the operation of the pumps, air blowers, motors, ventilation
fans and extraction fans of deodorisation units, etc. in the upgraded
TPSTW. The pumps, air blowers and motors would be located within reinforced
concrete buildings, while ventilation fans would be provided at the ventilation
vents of these buildings. The upgraded TPSTW will be operated 24 hours
per day, 7 days per week throughout the year. Since no NSR is identified
within the 300m assessment boundary of this Project, no unacceptable
operational fixed plant noise impact would be expected due to this Project.
12.6.7 The fixed plants of the proposed THEES
upgrading and OWPC would be located over 500m from the closest representative
NSR of this Project (i.e. the planned residential development at Ting Kok).
According to the information presented in the EIA Report for SWGC (EIAO
Register No. AEIAR-221/2019), one fixed plant of the proposed SWGC is located
about 200m from the closest representative NSR of this Project (i.e. planned
residential development at Ting Kok) but this fixed plant is over 300m from the
boundary of this Project. Due to the large buffer distance, unacceptable
cumulative operational noise impact would not be expected.
12.6.8 During operational phase of the Project,
vehicles from the Project site would pass Dai Cheong Street to Ting Kok Road or Yuen Shin Road. The
maximum number of vehicles due to the operation of the upgraded TPSTW is
anticipated to be 10 nos. vehicles per hour. Therefore, the increased
noise level due to the operation of the upgraded TPSTW at Ting Kok Road and
Yuen Shin Road would be insignificant. Unacceptable off-site road traffic
impact would not be expected.
12.7
Mitigation Measures
Construction Phase
12.7.1 The
following good site practices should be adopted during construction of the
Project to minimise noise impact to the surroundings:
ĄP Only well-maintained plant should be operated on-site and plant should
be serviced regularly during the construction phase;
ĄP Silencers or mufflers on construction equipment should be utilised and
should be properly maintained during the construction phase;
ĄP Mobile plant should be sited as far away from sensitive uses as
possible;
ĄP Machines and plant (such as trucks) that may be in intermittent use
should be shut down between work periods or should be throttled down to a
minimum;
ĄP Plant known to emit noise strongly in one direction should, wherever
possible, be orientated so that the noise is directed away from sensitive uses;
ĄP Material stockpiles and other structures should be effectively utilised,
wherever practicable, in screening noise from on-site construction activities.
And
ĄP Noisy construction activities such as road surface breaking, should be
scheduled to less sensitive hours during the day, e.g. midday, as far as
practicable.
12.7.2 The feasibility of adopting quieter construction methods and
use of quieter and more environmentally friendly construction equipment listed
in EPD website should be considered and explored
to minimize the construction noise impact to the surroundings.
Operational Phase
12.7.3
During operation, the
noise emitting plants (pumps, air blowers, etc.) would be enclosed within
building structures. Since no existing, committed and planned NSR was
identified within assessment area of the Project, there would be no adverse noise impact generated
from the Project operation. No mitigation measure is proposed.
12.8
Environmental Monitoring and Audit Requirements
12.8.1
Since no existing, committed or planned NSR is identified within the
assessment area, noise monitoring and audit is considered unnecessary.
12.9
Conclusion
12.9.1 Noise impact generated
from the Project has been reviewed. Based on the latest available
information, no existing, committed or planned NSR is identified within the
300m assessment area. No unacceptable noise impact would be
generated from the construction and operation of the Project.