4.                   GROUND-BORNE NoISE

 

Introduction

 

4.1               In this section, the requirements, methodology, equipment, monitoring locations, criteria and protocols for the monitoring and audit of ground-borne noise impacts during the construction and operation phases of the Project are presented.

 

Methodology and Criteria

 

4.2               The construction ground-borne noise level should be measured in terms of the A-weighted equivalent continuous sound pressure level (Leq).  Leq (30 minutes) should be used as the monitoring parameter for the time period between 0700 and 1900 hours on normal weekdays. 

 

4.3               Supplementary information for data auditing and statistical results such as L10 and L90 should also be obtained for reference.  A sample data record sheet is shown in Appendix B for reference.

 

4.4               With reference to the Technical Memorandum for the Assessment of Noise from Places Other Than Domestic Premises, Public Places or Construction Sites (IND-TM) issued under the Noise Control Ordinance (NCO), the criteria for noise transmitted primarily through the structural elements of a building or buildings should be 10dB(A) less than the relevant Acceptable Noise Level (ANL). 

 

4.5               Between 1900 and 0700 hours and all day on Sundays and public holidays, activities involving the use of powered mechanical equipment (PME) for the purpose of carrying out construction work is prohibited unless a Construction Noise Permit (CNP) has been obtained.  A CNP may be granted in cases of noise being contained within the ANL at the NSRs.  ANLs are assigned depending upon the Area Sensitivity Ratings (ASRs).  The criteria applicable to ground-borne noise are summarised in Table 4.1 below.

 

Table 4.1      Ground-borne Construction Noise Criteria

 

Ground-borne Construction Noise Criteria, dB(A)


GBNSR Description

Daytime

(0700-1900 hrs)
(except General Holidays & Sunday)

Daytime during general holidays and Sundays and all days during Evening
(1900 to 2300 hrs)

Night-time
(2300 to 0700 hrs)

A

B

C

A

B

C

Education institutions

 

60/55 [a]

50

55

60

[b]

Domestic premises, hotels

 

65

50

55

60

35

40

45

Churches/temples, libraries, courts, performing arts, clinics

60

50

55

60

[b]

                Notes:

                [a] A 5dB(A) reduction in the ground-borne noise criterion is recommended for school during examination period.

                [b] No sensitive use during this period.

 

Monitoring Equipment

 

4.6               According to the requirements of the Technical Memorandum (TM) issued under the NCO, sound level meters in compliance with the International Electrotechnical Commission Publications 651: 1979 (Type 1) and 804: 1985 (Type 1) specifications should be used for carrying out the noise monitoring.  Immediately prior to and following each noise measurement the accuracy of the sound level meter should be checked using an acoustic calibrator generating a known sound pressure level at a known frequency.  Measurements may be accepted as valid only if the different between the calibration levels obtained before and after the noise measurement is less than 1.0 dB.

 

4.7               Noise measurements should not be made in the presence of wind with a steady speed exceeding 5ms-1 or wind with gusts exceeding 10ms-1. The wind speed should be checked with a portable wind speed meter capable of measuring wind speeds in m/s.

 

4.8               The ET Leader is responsible for the provision of the monitoring equipment.  He should ensure that sufficient noise measuring equipment and associated instrumentation are available for carrying out the baseline monitoring, regular impact monitoring and ad hoc monitoring.  All the equipment and associated instrumentation should be clearly labelled.

 

Monitoring Locations

 

4.9               In the EIA, it is predicted that the construction ground-borne noise will comply with the stipulated noise criteria at all ground-borne noise sensitive receivers (GBNSRs), except four GBNSRs in proximity to tunnel boring machine (TBM) operation.  The designated construction ground-borne noise monitoring locations with predicted noise levels equal to 65dB(A) or above are listed in Table 4.2 and their locations are shown in Figure Nos. NOL/ERL/300C/XRL/ENS/M62/300 to 304.

 

Table 4.2      Construction Ground-borne Noise Monitoring Locations

GBNSR No. in EIA

Monitoring Location*

Uses

GN3

Yaumati Catholic Primary School (Hoi Wang Road)

Educational Institution

GN5

Tower 5, Park Avenue

Residential

GN7

Tai Fung Building (Block F) Cosmopolitan Estates

Residential

GN8

Chung Yew Building

Residential

GN31

DD110 LOT 482, Wang Toi Shan

Residential

Remark:

* The monitoring station should be at the lowest sensitive floor of each designated monitoring location.

 

4.10            The status and location of noise sensitive receivers may change after this manual is issued.  In such event, and if changes to the monitoring locations are considered necessary, the ET Leader should propose alternative monitoring locations and seek approval from the ER and agreement from the IEC and EPD on the proposal.  When alternative monitoring locations are proposed, the monitoring locations should be chosen based on the following criteria:

 

§          Monitoring at sensitive receivers close to the major site activities that are likely to have noise impacts;

§          Monitoring close to the noise sensitive receivers as defined in the Technical Memorandum; and

§          Assurance of minimal disturbance to the occupants during monitoring in the vicinity of sensitive receivers.

 

4.11            The monitoring station should be at the lowest sensitive floor of each designated monitoring location and normally be at a position 1.2m above ground inside the building structures.  If there is a problem with access to the normal monitoring position, an alternative position should be chosen, and a correction to the measurement results should be made.  The ET Leader should agree with the IEC and EPD on the monitoring position and the corrections adopted.  Once the positions for the monitoring stations are chosen, the baseline monitoring and the impact monitoring should be carried out at the same positions.

 

Baseline Monitoring

 

4.12            Background ground-borne noise should be measured inside the GBNSRs before the commencement of operation of the TBM.  The baseline ground-borne noise levels should be measured for a continuous period of at least 7 consecutive days at a minimum logging interval of 30 minutes for daytime (between 0700 and 1900 hours of normal weekdays) and 15 minutes (as three consecutive Leq, (5 minutes) readings) for evening time (between 1900 and 2300 hours on normal weekdays), general holidays including Sundays (between 0700 and 2300 hours) and night-time (between 2300 and 0700 of all days). The Leq, L10 and L90 should be recorded at the specified interval.  A schedule for the baseline monitoring should be submitted to the IEC for approval before the monitoring starts.  

 

4.13            There should not be any construction activities in the vicinity of the monitoring stations during the baseline monitoring.  Any non-Project related construction activities in the vicinity of the monitoring stations during the baseline monitoring should be noted and the source and location of such activities should be recorded.

 

4.14            In exceptional cases, when insufficient baseline monitoring data or questionable results are obtained, the ET Leader should liaise with the IEC and EPD to agree on an appropriate set of data to be used as a baseline reference.

      

Impact Monitoring

 

Construction Phase

 

4.15            Construction ground-borne noise monitoring plan should be provided by the ET and submitted to IEC and EPD for approval before the commencement of operation of the TBM.  Continuous impact ground-borne noise should be monitored at the GBNSRs when the TBM head is operating underneath the designated monitoring locations to audit EIA findings and monitor the noise impact. 

 

4.16            To account for cases in which ambient noise levels, as identified by the baseline monitoring, approach or exceed the stipulated Limit Levels presented in Table 4.1 prior to commencement of construction, a Maximum Acceptable Impact Level, which incorporates the baseline noise levels and the identified construction noise Limit Level, may be defined and agreed with EPD. The amended level will represent the maximum acceptable noise level at a specific monitoring station.

 

4.17            Table 4.3 presents the proposed TBM operating hours in relation to the measured ground-borne noise levels recorded at monitoring locations of different uses.   

Table 4.3      Proposed TBM Operating Time

Case

Monitoring Period

Monitoring Results

Acceptable Operating Time of TBM

Domestic Premises

1

0700 – 1900 hours

60 dB(A) < MNL(1) < 65(2) dB(A)

Daytime (Except general holidays and Sundays) (0700 – 1900 hrs) only

2

1900 – 2300 hours

MNL < 50/55/60(3) dB(A)

 

Daytime and evening time including general holidays and Sundays and all days during evening (0700-2300 hrs) only(4)

3

2300 – 0700 hours

MNL < 35/40/45(3) dB(A)

No restriction(4)

Schools, Temples or other sensitive receivers

4

0700 – 1900 hours

55 dB(A) < MNL < 60(2) dB(A)

Daytime, evening and night-time period (including general holidays and Sundays) (1900 – 0700 hrs) only(4)

5

1900 – 2300 hours

MNL < 55(2) dB(A)

No restriction(4)

Remark:

(1) MNL means Measured Noise Level.  If MNL is higher than the Limit level, the ET should inform the affected NSRs the proposed working hour and period of TBM operation.

(2) Limit level subject to background noise measurement results.  Highest noise level will be adopted as the upper limit.

(3) Noise criteria for Area Sensitive Rating “A”, “B” and “C” respectively.

(4) The operating time of TBM only applies for those receivers without sensitive use during restricted hours and subject to the granting of Construction Noise Permit and usages of the sensitive receivers and nearby GBNSRs.

 


 Operation Phase

 

4.18            With the predicted operation ground-borne noise levels complying with the stipulated noise criteria at all GBNSRs, mitigation measures are not required during the operation phase.  A noise commissioning test should be conducted by the ET prior to the operation of the Project to confirm the compliance of the operational ground-borne noise levels with the NCO noise criteria.  The noise commissioning test should be performed at selected key noise sensitive receivers including at least but not limited to the GBNSRs listed in Table 4.2.

 

4.19            A summary of the operational ground-borne noise criteria for the ground-borne GBNSRs is given in Table 4.4.

 

Table 4.4      Operational Ground-borne Noise Criteria

 

Ground-borne Railway Noise Criteria, dB(A)


GBNSRs Description

Day and Evening
Periods

(0900 to 2300 hrs)

Night-time Period
(2300 to 0700 hrs)

A

B

C

A

B

C

Churches/temples, schools,  medical clinics, libraries and courts

50

55

60

[a]

Domestic premises, hotels and hospitals

 

50

55

60

40

45

50

                Note:

                [a] No sensitive use during this period.

 

Mitigation Measures

 

Construction Phase

 

4.20            In addition to the proposed ground-borne noise monitoring and proper scheduling of works, close liaison with affected parties during the operation of the TBM is proposed to minimise the noise impact to the GBNSRs.  Prior to the commencement of the operation of the TBM, the following information in relation to the Project should be provided to nearby residents, schools and property owners:

 

§          the implementation programme of the tunnelling works;

§          the planned construction activities that will be involved;

§          the possible environmental impacts on the affected communities;

§          the monitoring programme to check the ground-borne noise construction noise levels; and

§          the communication channels between the local communities and the Project’s community liaison office to enhance communication with the public on the impacts and the necessity for enhancement of the measures.

 

4.21            It is considered that a close relation with local communities would be instrumental in ensuring that the works are carried out in an environmentally acceptable manner and to the satisfaction of the local communities environmental, and that environmental non-compliance is promptly dealt with in a transparent manner during construction.   A 24-hour hotline manned by the Contractor should be set up to maintain good communications and provide immediate responses.  All received enquiries or complaints should be logged immediately and forwarded to the relevant project officers for follow-up.

 

4.22            Prior to the final design of the trackform and the extent of each type of trackform, and after the proposed train in operation outside Hong Kong, tests of the FDL of the train should be carried out to update the ground-borne noise prediction and the recommendation on mitigation measures as necessary.

 

4.23            The vibration borehole testing should be carried out at two carefully selected locations along the proposed tunnel alignment prior to the commencement of construction works in order to determine the LSR values under certain geological conditions.  This will also allow further update of the ground-borne noise predictions and the recommendation on mitigation measures as necessary. 

 

Operation Phase

 

4.24            With the predicted operation ground-borne noise levels complying with the stipulated noise criteria at all GBNSRs, mitigation measures are not required during operation phase.   Installation of low noise trackform is recommended at several locations to further reduce the ground-borne noise levels to account for uncertainty of FDL and LSR values.