4.0 Marine
Water Quality Monitoring
4.1 Monitoring Locations
The
EIA conducted for the Project has identified a number of monitoring locations
that may portentially be affected by construction and operational activities as
summarized in Table 4.1 and shown in Figure TS 2031.
Table 4.1 Summary
of Monitoring Locations
Station |
Easting |
Northing |
M1 |
806244 |
827080 |
M2 |
806329 |
826408 |
M3 |
806235 |
826089 |
C1 |
806116 |
827618 |
C2 |
806034 |
825308 |
Control
station C1 should be the upstream control station for all monitoring stations
during mid-ebb and Control Station C2 should be the upstream control station
for all monitoring stations during mid-flood.
4.2
Monitoring Parameters
Monitoring
parameters for marine water quality monitoring have been set out in the Project
are summarized as follow:
Table 4.2 Marine water quality monitoring parameters
Parameter |
Duration |
No. of Locations |
Depth |
Dissolved Oxygen, DO (mg/L) |
2 tides/day, 3 days/week |
5 |
3 |
Turbidity (NTU) |
|||
Suspended Solids (mg/L) |
4.3 Environmental Quality Performance Limits
The marine
water quality criteria, namely Action and Limit (A/L) levels, determined according to the baseline study carried
out by ET are presented in the table below.
Table 4.3 Water Quality Action and Limit Levels
Parameter |
Action Level |
Limit Level |
Dissolved Oxygen (DO), mg/L |
Surface & Middle 4 mg/L Bottom 2.86 mg/L |
Surface & Middle 4 mg/L Bottom 2 mg/L |
Suspended Solids (SS), mg/L (Depth-averaged) |
44 mg/L or 120% of the upstream control
station’s SS at the same tide on the same day |
49 mg/L or 130% of the upstream control
station’s SS at the same tide on the same day |
Turbidity, NTU (Depth-averaged) |
37.4 NTU or 120% of the upstream control
station’s turbidity at the same tide on the same day |
46.2 NTU or 130% of the upstream control
station’s turbidity at the same tide on the same day |
4.4 Event-Action Plans
Event-Action Plans are
presented in Appendix E.
4.5 Monitoring
Results: Non-compliance against Action/Limit Levels
The results of DO, turbidity and SS are interpreted and
present in terms of tidal depth average. The summary of marine water quality
exceedances over the course of the Project is shown in Table 4.4.
Table 4.4 Summary
of Marine Water Quality Exceedances over the course of the Project
Station |
Exceedance
Level |
DO |
Turbidity |
SS |
|||
Flood |
Ebb |
Flood |
Ebb |
Flood |
Ebb |
||
C1 |
Action |
0 |
0 |
0 |
0 |
0 |
0 |
Limit |
0 |
0 |
1 |
0 |
1 |
0 |
|
M1 |
Action |
0 |
0 |
0 |
1 |
0 |
0 |
Limit |
0 |
0 |
1 |
0 |
1 |
0 |
|
M2 |
Action |
0 |
0 |
0 |
1 |
0 |
0 |
Limit |
0 |
0 |
1 |
0 |
1 |
0 |
|
M3 |
Action |
0 |
0 |
0 |
0 |
0 |
0 |
Limit |
0 |
0 |
1 |
0 |
1 |
0 |
|
C2 |
Action |
1 |
0 |
0 |
0 |
0 |
0 |
Limit |
0 |
0 |
1 |
0 |
1 |
0 |
|
Total |
Action |
1 |
0 |
0 |
2 |
0 |
0 |
Limit |
0 |
0 |
5 |
0 |
5 |
0 |
According to the summary of marine water monitoring results,
thirteen exceedances of DO, Turbidity and SS were recorded during the Project.
4.6
Graphical Plots and Statistical Analysis
of the trends of monitored parameters during the Project
The
Graphical Plots shown in Appendix B represent the trends in DO (Surface &
Middle and Bottom), Turbidity and SS during the course of the Project including
the baseline monitoring and post-project monitoring.
According
the graphical plots of the monitored parameters, it is found that a few
exceedances of surface-middle DO, Turbidity and SS were recorded during the
reporting period but they are not work-related. Since the trends of graphics of
monitored parameters at baseline monitoring, impact monitoring and post-project
monitoring are almost the same, this indicates that no adverse environmental
impact was introduce to the surrounding environment from the construction
works.
4.7
Explanation of Exceedances
Monitoring Date |
Tide |
Exceedance parameters |
Locations |
Explanation |
Implementation of Event and Action Plan |
13/06/03 |
Mid-ebb |
Turbidity |
M2 |
After ET’s investigation, it was found that no
construction works were carried out. No visible foam, oil, grease, litter or
other objectionable matter were observed near the construction site.
Therefore, it has proved that the exceedance was not related to the
construction work. |
After discussing with the RE, the IE and the Contractor,
it was concluded that no further mitigation measures should be taken since
the exceedance was not works-related. |
20/06/03 |
Mid-flood |
Dissolved Oxygen |
C2 |
After the ET’s investigation and discussion between the IE
and ET, C2 was up-stream control station during mid-flood and the exceedance
of dissolved oxygen (Surface and Middle) was not due to the construction
works. |
After discussing with the RE, the IE and the Contractor,
it was concluded that no further mitigation measures should be taken since
the exceedance was not works-related. |
27/06/03 |
Mid-flood |
Turbidity and Suspended Solids |
C1, M1, M2, M3 and C2 |
After ET’s investigation, it was found that no
construction works were carried out. No visible foam, oil, grease, litter or
other objectionable matter were observed near the construction site. During
the monitoring, ET found that the wave was so strong that settled solids were
stirred up from the seabed to the water column. Therefore, the exceedance was
not work-related. |
After discussing with the RE, the IE and the Contractor,
it was concluded that no further mitigation measures should be taken since
the exceedance was not works-related. |
03/11/03 |
Mid-Ebb |
Turbidity |
M1 |
During the marine water quality
monitoring at 03/11/2003, ET found that the major construction works was
demolishing existing pier. No visible foam, oil, grease, litter or other
objectionable matter were observed near the monitoring stations. Comparing
the monitoring results of the same tide, the turbidity at M1 was lower than
120% of upstream control station C1. Besides, the Turbidity result at
monitoring station M2 which is closer to the existing pier was found lower
than monitoring station M1 and within the Action and Limit Level, indicating
that the water quality impact due the construction works was not significant
and did not cause adversely effect on water quality near the site. Therefore,
the exceedance was not work-related. |
After discussing with the
IEC and the Contractor, it was concluded that no further mitigation measures
should be taken since the exceedance was not works-related. |