Agreement No. CE 23/2012 (EP)
Environmental Monitoring and Audit
for Contaminated Mud Pits to the South of The Brothers
and at East Sha Chau
(2012-2017) - Investigation
36th MONTHLY PROGRESS REPORT FOR August 2015
1.1.1
Since early 1990s,
contaminated sediment ([1]) arising from various
construction works (e.g. dredging and reclamation projects) in Hong Kong has been disposed of at a series of seabed pits
at East of Sha Chau (ESC). In late 2008, a review indicated that the
existing and planned facilities at ESC would not be able to meet the disposal
demand after 2012. In order to meet this
demand, the Hong Kong Special Administrative Region Government (HKSARG) decided
to implement a new contained aquatic disposal (CAD) ([2]) facility at the
South of The Brothers (SB CMPs) which had been under consideration for a number
of years.
1.1.2
The environmental
acceptability of the construction and operation of the Project had been
confirmed by findings of the associated Environmental Impact Assessment (EIA)
study completed in 2005 under Agreement No. CE 12/2002(EP) ([3]). The Director of Environmental Protection
(DEP) approved this EIA report under the Environmental Impact Assessment
Ordinance (Cap. 499) (EIAO)
in September 2005 (EIA Register No.: AEIAR-089/2005).
1.1.3
In accordance with
the EIA recommendation, prior to commencement of construction works for the SB
CMPs, the Civil Engineering and Development Department (CEDD) undertook a
detailed review and update of the EIA findings for the SB site ([4]).
Findings of the EIA review undertaken in 2009/ 2010 confirmed that the
construction and operation of the SB site had been predicted to be
environmentally acceptable.
1.1.4
Environmental Permits (EPs) (EP-312/2008/A and EP-427/2011A) were issued by the Environmental Protection Department
(EPD) to the CEDD, the Permit Holder, on 28 November 2008 for ESC CMP V and on
23 December 2011 for SB CMPs, respectively.
Under the requirements of the EPs,
an Environmental Monitoring and Audit (EM&A) programme as set out in the
EM&A Manuals ()
()
is required to be implemented for the CMPs.
1.1.5
The present
EM&A programme under Agreement No. CE 23/2012 (EP) covers the dredging, disposal and capping operations of the
SB CMPs as well as ESC
CMPs. Detailed works
schedule for both CMPs is shown in Figure 1.1. In August 2015, the
following works were being undertaken at the CMPs:
·
Capping
operations at ESC CMPs;
·
Capping
operations at SB CMP 1; and
·
Disposal of
contaminated mud at SB CMP 2.
Figure 1.1 Works
Schedule for ESC CMPs and SB CMPs
1.2
Reporting Period
1.2.1
This 36th
Monthly Progress Report covers the
EM&A activities for the reporting month of August
2015.
1.3
Details of Sampling and Laboratory Testing
Activities
1.3.1
The following
monitoring activities have been undertaken for ESC CMPs in August 2015:
·
Benthic Recolonisation Studies of ESC CMPs was undertaken on
12 August 2015; and
·
Water
Quality Monitoring During Capping of ESC
CMPs was undertaken on 18 August 2015.
1.3.2
The following
monitoring activities have been undertaken for SB CMPs in August 2015:
· Water
Column Profiling of CMP 2 was undertaken on
10 August 2015;
· Routine
Water Quality Monitoring of CMP 2 was undertaken on 13 August 2015;
· Pit
Specific Sediment Chemistry of CMP 2 was undertaken on
17 August 2015;
· Demersal Trawling for CMPs was undertaken on 19 and 20 August 2015;
· Cumulative Impact
Sediment Chemistry of CMP 2 was
undertaken on 19 and 21 August 2015;
· Sediment
Toxicity Test of CMP 2
was undertaken on 19 and 21 August 2015;
· Water Quality
Monitoring During Capping of CMP 1 was
undertaken on 24 August 2015; and
· Benthic Recolonisation Studies of CMP 1 was undertaken on 26 August 2015.
1.4
Details of Outstanding Sampling and/or
Analysis
1.4.1
No outstanding sampling remained for August 2015.
1.4.2
A summary of field activities conducted are presented
in Annex A. The following laboratory
analyses were still in progress during the preparation of this monthly report
and hence are not presented in this monthly report:
·
Laboratory analyses of sediment samples collected for Cumulative
Impact Sediment Chemistry of SB CMP 2 in August 2015; and
·
Laboratory analyses of sediment samples collected for Pit
Specific Sediment Chemistry of SB CMP 2 in August 2015.
1.4.3
The following laboratory analyses are in progress and
will be presented in the corresponding quarterly report:
· Laboratory
analyses of sediment samples collected for Benthic Recolonisation
Studies of ESC CMPs and SB CMP 1 in
August 2015;
· Taxonomic identification of fishery resources
collected during Demersal Trawling for
SB CMPs in July and August 2015; and
· Laboratory
analyses for Sediment Toxicity Test of SB CMP 2 in August 2015.
1.5
Brief Discussion of the Monitoring Results
for ESC CMPs
1.5.1
Brief discussion of the
monitoring results of the Water Quality Monitoring during Capping of ESC CMPs conducted in August 2015
is presented below. Graphical presentation of the monitoring results is provided
in Annex B.
1.5.2
Water
Quality Monitoring during Capping of ESC
CMPs – August 2015
1.5.3
The monitoring results obtained during August 2015 sampling in the wet season have been assessed for
compliance with the Water Quality Objectives (WQOs) set by Environmental Protection Department (EPD). This consists of a review of the EPD routine water quality
monitoring data for the wet season period (April to October) of 2004 - 2013 from stations in the Northwestern
Water Control Zone (WCZ), where the CMPs are located (). For Salinity, the averaged value obtained from
the Reference stations was used for the basis as the WQO. Levels of
Dissolved Oxygen (DO) and Turbidity were also assessed for compliance with the
Action and Limit Levels (see Table C1 of Annex C for details). A total of ten (10) monitoring stations were sampled in August 2015 as
shown in Figure
1.2.
In-situ
Measurements
1.5.4
Graphical presentation of the monitoring results (Temperature, DO, pH, Salinity and Turbidity) is shown in Figures 1-6 of Annex B. Levels of
Dissolved Oxygen (DO) and pH at all stations in August 2015 complied with the WQO and the Action and Limit levels (Table C1 of Annex C). Level of Salinity
at most station also complied with WQO, except for Ma Wan station. The higher Salinities
recorded at Ma Wan station are likely to be caused by the larger separation
distance to Pearl River mouth, which release a large amount of freshwater
runoff in the area during flooding, when compared to the Reference stations.
Laboratory
Measurements for Suspended Solids (SS)
Concentrations of SS complied with the WQO at all
stations in August 2015, except for the Impact stations (Figure 7 of Annex B; Table C2 of Annex C). However, concentrations of SS at all stations
complied with the Action and Limit Levels.
Further statistical analysis will
be undertaken in the quarterly report to investigate whether the capping
operations at ESC CMPs is causing any unacceptable deterioration in water
quality of the area.
1.6.1
Brief discussion of the monitoring results of
the following activities for SB CMPs is presented in this 36th
Monthly Progress Report:
· Water Quality
Monitoring During Capping of CMP 1 in August
2015;
· Water
Column Profiling of CMP 2 in August 2015; and
· Routine Water
Quality Monitoring of CMP 2 in August
2015.
1.6.2
Water
Quality Monitoring during Capping of SB
CMP 1 – August 2015
1.6.3
The monitoring results obtained during August 2015 sampling in the wet season have been assessed for
compliance with the WQOs (see Section 1.5.3 for details). Levels of DO and
Turbidity were also assessed for compliance with the Action and Limit Levels (see Table C3 of Annex C for details). A total of fourteen (14) monitoring stations were sampled in August 2015 as shown in Figure
1.3. Graphical
presentation of the monitoring results is provided in Annex B.
In-situ
Measurements
1.6.4
Graphical presentation of the monitoring results
(Temperature, DO, pH, Salinity and Turbidity) is shown in Figures 8-13 of Annex B. Levels of pH at all stations in August 2015 complied with the WQO. DO at most stations complied
with the WQO except at Sham Shui Kok station. However, the levels of DO at all stations
complied with the Action and Limit levels in August 2015 (Table C3 of Annex C). In addition, and the levels
of Turbidity complied with the Action and Limit levels at all
stations in August 2015 (Table C3 and C4 of Annex C).
1.6.5
Levels of Salinity at most stations complied with the WQO except
at Intermediate, Sham Shui Kok, Tai Ho Bay 2 and Ma Wan stations. The lower
Salinities recorded at Tai Ho Bay 2 and Reference
stations are likely due to the close proximity of the nearby streams, which
release large amount of freshwater runoff in the area during flooding. The Salinities at other stations were higher or above the WQO as they were located further away from the Tai
Ho Bay and Reference stations which experienced less freshwater runoff from the
nearby streams.
Laboratory
Measurements
1.6.6
Concentrations of
SS complied with the WQO (11.6 mg/L for wet season) at
Intermediate,
Ma Wan and Tai Ho Bay 2 stations, but not at Reference, Impact, Tai Ho Bay 1 and Sham Shui
Kok stations in August 2015 (Figure 14 of
Annex B). However, SS at all stations
complied with the Action and Limit Levels in August 2015 (Table C3 and C4 of Annex C).
1.6.7
For nutrients,
concentrations of Ammonia (NH3) were relatively similar amongst most stations except a slightly lower value was
recorded at Tai Ho Bay 2 station (Figures 15 of Annex B). Total Inorganic Nitrogen (TIN) at Impact,
Reference, Tai Ho Bay 1 and Tai Mo To stations exceeded the WQO of 0.5 mg/L in August 2015 (Figure 16 of Annex B). It should be noted that the
North Western WCZ has historically experienced higher levels of TIN and the exceedances of TIN WQO at these stations are
unlikely to be caused by the capping operation at CMP 1.
1.6.8
Concentrations of
Biochemical Oxygen Demand (BOD5) were similar at most stations except higher values were recorded at Reference
stations in August 2015 (Figures 17 of Annex B).
1.6.9
Statistical
analysis will be undertaken and presented in the quarterly report to
investigate whether the capping operations at CMP 1 is causing any unacceptable
impacts in water quality of the area.
1.6.10
Routine
Water Quality Monitoring of SB CMP 2 – August 2015
1.6.11
The monitoring
results for the Routine Water Quality Monitoring conducted in August 2015 in the wet season
have been assessed for compliance with the WQOs (see Section
1.5.3 for details). Levels of
Dissolved Oxygen (DO) and Turbidity were also assessed for compliance with the
Action and Limit Levels (see Table C3 of Annex C for details).
The monitoring results are shown in Figures 18-28 of Annex B and Tables
C5 and C6 of Annex C. A total of twenty
(20) monitoring stations were sampled in August 2015 as shown in Figure 1.4.
In-situ
Measurements
1.6.12
Graphical presentation of the monitoring results
(Temperature, DO, pH, Salinity and Turbidity) is shown in Figures 18-23 of Annex B. Analyses of
results for August 2015 indicated that
the levels of pH and DO complied with the
WQOs at all stations (Impact, Intermediate, Reference and Water Sensitive
Receiver stations) in August 2015 (Figures 18 – 20 of Annex B).
1.6.13
The levels of
Salinity at Impact, Intermediate and Water Sensitive Receiver stations exceeded
the WQO range in August 2015 (Figure
22
of Annex B). The lower
Salinities recorded at these stations, which lead to exceedance of the WQO, is
likely to be caused by the freshwater discharged from the Pearl River Delta
during the summer months which tend to form a surface layer of low salinity
water at these stations with shallower depth when compared with the Reference
stations.
1.6.14
The levels of DO
and Turbidity complied with the Action and Limit Levels at all stations (Figures
19 and 22 of Annex
B; Table C5 of Annex
C).
1.6.15
Overall, in-situ measurement results of the Routine Water
Quality Monitoring indicated that the
disposal operation at CMP 2 did not appear to cause any unacceptable impacts in water quality in August 2015.
Laboratory
Measurements
1.6.16
Laboratory analysis of August 2015 results indicated that concentrations of Cadmium,
Chromium, Silver and Mercury were below their limit of reporting at all stations. Arsenic, Copper, Lead, Nickel and Zinc were
detected in August 2015 samples and the concentrations were similar
amongst stations (Figures 24-25 of Annex B). Results of laboratory analysis were shown in Table C6 of Annex C.
1.6.17
For nutrients, concentrations of TIN at all stations
in August 2015 exceeded the WQO
(0.5mg/L) (Figure 26 of Annex B). As discussed in Section 1.6.7, the North Western
WCZ has historically experienced higher levels of TIN and the
exceedances of TIN WQO at all stations in August 2015 were unlikely to be caused by the disposal operation
at CMP 2. Ammonia Nitrogen (NH3-N) concentration
was relatively similar amongst all stations (Figure 26 of Annex B). Levels of 5-day Biochemical Oxygen Demand (BOD5) appear
to be higher at Tai Ho Bay 1 and Shum Shui Kok stations in August 2015 (Figure 27 of Annex B).
1.6.18
Concentrations of SS complied the WQO (11.6 mg/L for wet season) at all stations, except
Reference stations in August 2015.
Concentrations of SS complied with the
Action and Limit Levels at all stations in August 2015 (Figure 28 of Annex B; Table
C6 of Annex C).
1.6.19
Overall, results
of the Routine Water Quality Monitoring indicated that the disposal operation at CMP 2 did not
appear to cause any unacceptable deterioration in water quality in August 2015. Detailed
statistical analysis will be presented in the Quarterly Report to investigate
any spatial and temporal trends of potential concern.
1.6.20
Water
Column Profiling of CMP 2 – August 2015
1.6.21
Water Column Profiling was undertaken at a total of two sampling stations
(Upstream and Downstream stations) on 10 August 2015. The water quality monitoring results have been assessed for
compliance with the WQOs as discussed in Section 1.5.3. The monitoring results
were also compared with the Action and Limit Levels
set in Baseline Monitoring Report (see Table C3 of Annex C for details).
In-situ Measurements
1.6.22
Analyses of results for August 2015 indicated that levels of Salinity,
DO and pH complied with the WQOs at both Downstream and
Upstream stations (Table C7 of Annex
C). In addition, DO and Turbidity at all stations
complied with the Action and Limit Levels (Tables C3 and C7 of Annex C).
Laboratory Measurements for SS
1.6.23
Analyses of results for August
2015 indicated that the SS
levels at both Upstream and Downstream stations complied with the WQO. Both Upstream and Downstream stations also
complied with the Action and Limit Levels (Tables C3 and C7 of Annex
C).
Overall,
the monitoring results indicated that the mud disposal operation at CMP 2 did
not appear to cause any deterioration in water quality during this reporting
period.
1.7
Activities Scheduled for the Next Month
1.7.1
The following monitoring activities will be conducted
in the next monthly period of September 2015 for SB CMPs:
· Pit
Specific Sediment Chemistry of CMP 2; and
· Water
Column Profiling of CMP 2.
1.7.2
The following monitoring activities will
be conducted in the next monthly period of September
2015 for ESC CMPs:
·
Impact
Monitoring during Dredging Operations of ESC CMPs.
1.7.3
The sampling schedule is presented in Annex A.
1.8.1
A summary of the Study programme is presented in Annex D.