3.1
In
accordance with the Updated EM&A Manual, impact 1-hour TSP and 24-hr TSP
monitoring were conducted to monitor the air quality for the Works Contracts. Appendix B shows the established Action/Limit
Levels for the air quality monitoring works.
3.2
Impact
1-hour TSP monitoring was conducted for at least three times every 6 days,
while the impact 24-hour TSP monitoring was conducted for at least once every 6
days at one air quality monitoring station.
3.3
Impact
air quality monitoring was conducted at the monitoring stations under the Works
Contracts, as shown in Figure 1 and
Figure 2 according to Table 1.1 of Updated EM&A Manual and Baseline Air
Quality Monitoring Report (KTN & FLN NDA). Table 3.1 describes the location of the air quality monitoring
station.
Table 3.1 Location for Air Quality Monitoring
Locations
|
EP No. |
Contract No. |
Monitoring Station |
Location |
|
EP-473/2013/A |
ND/2019/03 |
FLN-DMS1[2] |
Scattered Village Houses North of Proposed
Potential Ecopark |
|
ND/2019/04 |
|||
|
ND/2019/05 |
FLN-DMS3[3] |
House near Tong Hang |
|
|
ND/2019/03 |
FLN-DMS5[4]
FLN-DMS5A |
Noble Hill Good View New Village |
|
|
ND/2019/04 |
|||
|
EP-466/2013 EP-467/2013/A EP-468/2013/A |
ND/2019/01 |
KTN-DMS4 |
Temporary Structure near Fanling
Highway (near Pak Shek Au) |
|
EP-468/2013/A |
ND/2019/03 |
Remark:
[1]:
Noting that construction phase air quality monitoring at the other proposed
monitoring stations (e.g. planned), where access is permitted, will be
conducted during the relevant works contract(s).
[2]:
Since the distance between monitoring station and site boundary of ND/2019/05
under EP-473/2013/A exceeds 500m. The monitoring station is not applicable to
ND/2019/05.
[3]:
Since the distance between monitoring station and site boundary of ND/2019/03
and ND/2019/04 under EP-473/2013/A exceeds 500m. The monitoring station is not
applicable to ND/2019/03 and ND/2019/04.
[4]:
Since the distance between monitoring station and site boundary of ND/2019/05
under EP-473/2013/A exceeds 500m. The monitoring station is not applicable to
ND/2019/05
3.4
As
the power supply for High Volume Sampler (HVS) for TSP monitoring at FLN-DMS 5A
and KTN-DMS 4 were rejected, direct reading dust meter was used to measure both
1-hour and 24-hour average TSP levels:-
Ÿ
The
proposal for alternative monitoring equipment (i.e. direct reading dust meter)
for TSP monitoring was approved by EPD according to approved Baseline Air
Quality Monitoring Report (KTN & FLN NDA); and
Ÿ
Adopt
same measurement methodology (i.e. direct reading dust meter) as baseline
monitoring for reliable comparison.
3.5
The
proposed use of portable direct reading dust meters was submitted to IEC and
obtained agreement from the IEC as stated in Section 2.4.5 of the Updated
EM&A Manual.
3.6
HVS
for 24-hr TSP monitoring will be adopted once secured supply of electricity
become available at FLN-DMS 5A and KTN-DMS 4.
3.7
Table 3.2 summarizes the equipment used in
the impact air monitoring programme. Copies of calibration certificates are
attached in Appendix C.
Table 3.2 Air Quality Monitoring Equipment
|
Monitoring Station |
Equipment |
Manufacturer |
Model and Make |
Quantity |
|
FLN-DMS5A KTN-DMS4 |
Dust
Monitor (1-hour
and 24-hour TSP) |
Met One Instruments |
AEROCET-831 |
10 |
|
FLN-DMS1 FLN-DMS3 |
Dust
Monitor (1-hour
TSP) |
|||
|
HVS
Sampler (TSP) (24-hour
TSP) |
Tisch |
TISCH Model: TE-5170 |
2 |
3.8
Meteorological
information extracted from “Hong Kong Observatory - Ta Kwu Ling Weather
Station” was proposed as the alternative method to obtain representative wind
data. For Ta Kwu Ling Weather Station, it is located nearby the Project site
and situated at approximately 15m above mean sea level. The station’s wind data
monitoring equipment is set above the existing ground ten meters in compliance
with the general setting up requirement. Furthermore, this station also
provides other meteorological information, such as the humidity, rainfall, air
pressure and temperature etc.
3.9
The
general weather conditions (i.e. sunny, cloudy or rainy) were recorded by the
field staffs during the monitoring day.
3.10
Table 3.3 summarizes the monitoring parameters and frequencies of impact dust monitoring
during the Works Contracts activities. The air quality monitoring schedule for
the reporting month is shown in Appendix
D.
Table 3.3 Impact Dust Monitoring Parameters, Frequency and
Duration
|
Parameters |
Frequency |
|
1-hr
TSP |
Three
times/ 6 days |
|
24-hr
TSP |
Once /
6 days |
1-hour and 24-hour
TSP Air Quality Monitoring
Instrumentation
3.11
Direct reading
dust meter was deployed for the air quality monitoring as shown in Table 3.2.
3.12
The measuring
procedures of the dust meter are in accordance with the Manufacturer’s
Instruction Manual as follows:
(AEROCET-831)
•
The 1-hour dust
meter is placed at least 1.3 meters above ground.
•
Press and hold the
Power key momentarily to power on the unit and make sure that the battery level
was not flash or in low level.
•
Allow the
instrument to stand for about 3 second to display the Sample Screen minutes.
•
Press the START
/ STOP key to run the internal vacuum pump for 1 minute and ready to use.
•
Use the select
dial to select the PM range and press the START / STOP key to start a
measurement.
•
Finally, push
the START/STOP key to stop the measuring after 1 hour sampling.
•
Information
such as sampling date, time, value and site condition were recorded during the
monitoring period.
• All data were recorded in the data logger for
further data processing.
Maintenance/Calibration
3.13
The following
maintenance/calibration was required for the direct dust meters:
• Check and calibrate the meter by HVS to check the
validity and accuracy of the results measured by direct reading method at
2-month intervals throughout all stages of the air quality monitoring.
24-hour TSP Air
Quality Monitoring
Instrumentation
(TISCH Model: TE-5170)
3.14
High volume
Samplers (HVS) completed with appropriate sampling inlets were employed for
24-hour TSP monitoring. Each
sampler was composed of a motor, a filter holder, a flow controller and a
sampling inlet and its performance specification complies with that required by
USEPA Standard Title 40, Code of Federation Regulations Chapter 1 (Part 50).
HVS
Installation
3.15
The following
guidelines were adopted during the installation of HVS:
•
A horizontal platform
with appropriate support was provided to secure the samplers against gusty
wind.
•
No two samplers
were placed less than 2 meters apart.
•
The distance
between the sampler and an obstacle, such as buildings, was at least twice the
height that the obstacle protrudes above the sampler.
•
A minimum of 2
meters of separation from walls, parapets and penthouses was required for
rooftop samples.
•
A minimum of 2
meters separation from any supporting structure, measured horizontally was
required.
•
No furnaces or
incineration flues were nearby.
•
Airflow around
the sampler was unrestricted.
•
The samplers
were more than 20 meters from the drip line.
•
Any wire fence
and gate, to protect the sampler, should not cause any obstruction during
monitoring.
•
Permission and
access to the monitoring stations have been obtained to set up the samplers;
and
• A secured supply of electricity was provided to
operate the samplers.
Filters
Preparation
3.16
Wellab Limited
(HOKLAS Registration No.083) is the HOKLAS accredited laboratory and
responsible for the preparation of 24-hr conditioned and pre-weighed filter
papers for monitoring team.
3.17
All filters
were equilibrated in the conditioning environment for 24 hours before weighing. The conditioning environment temperature
was around
Operating/Analytical
Procedures
3.18
Operating/analytical
procedures for the air quality monitoring were highlighted as follows:
•
Prior to the
commencement of the dust sampling, the flow rate of the HVS was properly set
(between 1.1 m3/min. and 1.4 m3/min.) in accordance with
the manufacturer's instruction to within the range recommended in USEPA
Standard Title 40, CFR Part 50;
•
The power
supply was checked to ensure the sampler worked properly;
•
On sampling,
the sampler was operated for 5 minutes to establish thermal equilibrium before
placing any filter media at the designated air quality monitoring station;
•
The filter
holding frame was then removed by loosening the four nuts and carefully a
weighted and conditioned filter was centered with the stamped number upwards,
on a supporting screen;
•
The filter was
aligned on the screen so that the gasket formed an airtight seal on the outer
edges of the filter. Then the
filter holding frame was tightened to the filter holder with swing bolts. The applied pressure should be
sufficient to avoid air leakage at the edges;
•
The shelter lid
was closed and secured with the aluminum strip;
•
The timer was
then programmed. Information was
recorded on the record sheet, which included the starting time, the weather
condition and the filter number (the initial weight of the filter paper can be
found out by using the filter number);
•
After sampling,
the filter was removed and kept in a clean and tightly sealed plastic bag. The
filter paper was then be returned to the HOKLAS laboratory (Wellab Ltd.) for
reconditioning in the humidity-controlled chamber followed by accurate
weighting by an electronic balance with a readout down to 0.1mg. The elapsed
time was also recorded; and
• Before weighing, all filters were equilibrated in a
conditioning environment for 24 hours. The conditioning environment temperature
should be between
Maintenance/Calibration
3.19
The following
maintenance/calibration was required for the HVS:
•
The high volume
motors and their accessories were properly maintained. Appropriate maintenance
such as routine motor brushes replacement and electrical wiring checking were
made to ensure that the equipment and necessary power supply are in good
working condition; and
•
All HVS were
calibrated (five point calibration) using Calibration Kit prior to the
commencement of the baseline monitoring and thereafter at bi-monthly intervals.
3.20
The monitoring
results for 1-hour TSP and 24-hour TSP are summarized in Table 3.4 and
3.5, respectively. Detailed monitoring results and graphical presentations of
1-hour and 24-hour TSP monitoring results are shown in Appendix E.
Table 3.4 Summary
Table of 1-hour TSP Monitoring Results during the
Reporting Month
|
Monitoring Station |
Concentration (µg/m3) |
Action Level, µg/m3 |
Limit Level, µg/m3 |
|
|
Average |
Range |
|||
|
FLN-DMS1 |
97.0 |
81.1 – 127.9 |
303 |
500 |
|
FLN-DMS3 |
97.0 |
63.2 – 137.1 |
301 |
500 |
|
FLN-DMS5 |
81.7 |
61.7 – 113.9 |
279 |
500 |
|
KTN-DMS4 |
60.2 |
33.4 – 91.3 |
297 |
500 |
Table 3.5 Summary
Table of 24-hour TSP Monitoring Results during the
Reporting Month
|
Monitoring Station |
Concentration (µg/m3) |
Action Level, µg/m3 |
Limit Level, µg/m3 |
|
|
Average |
Range |
|||
|
FLN-DMS1 |
82.6 |
24.7 – 128.7 |
150 |
260 |
|
FLN-DMS3 |
56.3 |
19.2 – 75.6 |
165 |
260 |
|
FLN-DMS5A |
91.9 |
62.1 – 106.9 |
153 |
260 |
|
KTN-DMS4 |
60.7 |
37.2 – 106.5 |
192 |
260 |
3.21
All 1-hour and 24-hour
TSP monitoring was conducted as scheduled in the reporting month. No Action/Limit Level exceedances were
recorded.
3.22
According to
our field observations, the major dust source identified at the designated air
quality monitoring stations in the reporting month are shown in Table 3.6:
Table 3.6 Observation
at Dust Monitoring Stations
|
Monitoring Station |
Major
Dust Source |
|
FLN DMS1 |
Mobile
crane, Excavator, piling, road traffic |
|
FLN-DMS3 |
Excavator,
piling, mobile crane, road traffic |
|
FLN-DMS5 |
Road
traffic |
|
KTN-DMS4 |
Excavator,
piling, mobile crane, dump truck, road traffic |
3.23
Should
project-related non-compliance of the criteria occur, action in accordance with
the Action Plan in Appendix N shall
be carried out.