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
41st MONTHLY PROGRESS REPORT FOR January
2016
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 January 2016, the following works were
being undertaken at the CMPs:
· Dredging operation at ESC CMP Vd;
· Capping operation at ESC CMP Va; 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 41st
Monthly Progress Report covers the EM&A activities for
the reporting month of January 2016.
1.3
Details
of Sampling and Laboratory Testing Activities
1.3.1
The following monitoring activities have been undertaken for
ESC CMPs in January 2016:
· Impact Water Quality
Monitoring during Dredging Operations of ESC CMP Vd
was undertaken on 5 and 12 January 2016.
1.3.2
The following monitoring activities have been undertaken for
SB CMPs in January 2016:
·
Routine Water Quality Monitoring of CMP 2 was undertaken on 6 January 2016;
·
Pit Specific Sediment Chemistry of CMP 2 was undertaken on 7 January 2016;
·
Water Column Profiling of CMP 2 was undertaken on
11 January 2016; and
·
Demersal Trawling for SB CMP was undertaken on 18 and 19
January 2016.
1.4
Details
of Outstanding Sampling and/or Analysis
1.4.1
No outstanding sampling remained for January 2016.
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 Pit
Specific Sediment Chemistry of SB CMP 2 in January 2016.
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 Demersal Trawling for SB CMP in January 2016.
1.5
Brief
Discussion of the Monitoring Results for ESC CMPs
1.5.1
Brief discussion of the
monitoring results of the Impact Water Quality Monitoring during Dredging
Operations of ESC CMP Vd conducted in January 2016 is presented below.
1.5.2
Impact Water Quality Monitoring during Dredging Operations of ESC CMP Vd – January 2016
1.5.3
Dredging
activities were carried out on 2 – 4, 8,
12 and 13 January 2016 during this
reporting period and monitoring was conducted on 5 and 12 January 2016. On each survey day, monitoring was conducted
during both mid-ebb and mid-flood tides at two Reference (Upstream) stations
and five Impact (Downstream) stations around the dredging operations at ESC CMP Vd. Monitoring was
also conducted at one Sensitive Receiver station
situated in Ma Wan. A total of eight (8)
stations were monitored and locations of the sampling stations are shown in Figure 1.2.
1.5.4
Monitoring
results are presented in Table B1 of Annex B. Daily
dredging volume in January 2016 is reported in Annex C. Levels of
Dissolved Oxygen (DO), Turbidity and Suspended Solid (SS) complied with the
Action and Limit Levels (see Table B2
of Annex B for details) set in the Baseline
Monitoring Report ().
1.5.5
The
results indicated that the dredging operations at ESC CMP Vd
did not appear to cause any unacceptable deterioration in water quality during
this reporting period. Therefore, no
further action, except for those recommended in the Environmental Permit (EP-312/2008/A), are
considered necessary for the dredging operations.
1.6
Brief
Discussion of the Monitoring Results for SB CMPs
1.6.1
Brief discussion of the
monitoring results of the following activities for SB CMPs
is presented in this 41st
Monthly Progress Report:
·
Pit Specific Sediment Chemistry of CMP 2 in December 2015;
·
Cumulative Impact Sediment Chemistry of CMP 2 in December 2015;
·
Routine Water Quality Monitoring of CMP 2 in January 2016; and
·
Water Column Profiling of CMP 2 in
January 2016.
1.6.2
Pit Specific Sediment Chemistry of CMP 2 –
December 2015
1.6.3
Monitoring locations for Pit Specific Sediment Chemistry for CMP 2 are shown in Figure 1.3. A total of six (6)
monitoring stations were sampled in December 2015.
1.6.4
The concentrations of all inorganic contaminants (Arsenic,
Cadmium, Chromium, Copper, Lead, Mercury, Nickel, Silver and Zinc) were lower
than the Lower Chemical Exceedance Level (LCEL) at all stations (Figures 1 and
2 of Annex D).
1.6.5
For organic contaminants,
the concentrations of Total Organic Carbon (TOC) were similar at most stations
and it was observed to be higher at Active Pit station SB-NPBA and lower at
Active Pit station SB-NPBB (Figure 3 of
Annex D). Tributyltin (TBT)
concentrations were observed to be higher at Active Pit station SB-NPBA and
SB-NPBB (Figure 4 of Annex D). Low and High
Molecular Weight Polycyclic Aromatic Hydrocarbons (PAHs),
Total Polychlorinated Biphenyls (PCBs), 4,4’-dichlorodiphenyldichloroethylene
(DDE) and Total dichlorodiphenyltrichloroethane (DDT) concentrations were below
the limit of reporting at most stations, except High Molecular Weight PAHs at Active Pit stations SB-NPBA (Figure
5 of Annex D).
1.6.6
Overall, there is no
evidence indicating any unacceptable environmental impacts to sediment quality
as a result of the contaminated mud disposal operations at CMP 2 in December 2015. Statistical analysis will be undertaken and
presented in the quarterly report to investigate whether there are any
unacceptable impacts in the area caused by the contaminated mud disposal.
1.6.7
Cumulative Impact Sediment Chemistry of SB
CMPs – December 2015
1.6.8
Monitoring locations for Cumulative Impact Sediment Chemistry for SB CMPs are shown in Figure 1.4. A total of eleven (11) monitoring stations
were sampled in December 2015.
1.6.9
Analyses
of results for the Cumulative Impact Sediment Chemistry
Monitoring indicated that the
concentrations of all inorganic contaminants were below the LCEL in December 2015 (Figures 6 and 7 of Annex D).
1.6.10
For organic contaminants, concentrations of TOC at Near-field
station SB-RNA
and Mid-field stations SB-RMA and SB-RMB were recorded to be lower than other stations (Figure 8 of Annex
D).
Concentrations of TBTs were recorded to be
higher at Mid-field station SB-RMB and Ma Wan station (Figure 9 of Annex
D).
Total DDT, 4,4’-DDE, Total PCBs as well as Low and High Molecular Weight PAHs were recorded below the limit of
reporting at all stations.
1.6.11
Overall, there is no
evidence indicating any unacceptable environmental impacts to sediment quality
as a result of the contaminated mud disposal operations at CMP 2 in December 2015. Statistical
analysis will be undertaken and presented in the quarterly report to
investigate whether there are any unacceptable impacts in the area caused by
the contaminated mud disposal.
1.6.12
Routine Water Quality Monitoring of SB CMP
2 – January 2016
1.6.13
The monitoring results for
the Routine Water Quality Monitoring conducted in January 2016
in the dry 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 dry season
period (November to March) of 2005 - 2014 from stations in the Northwestern
Water Control Zone (WCZ), where the CMPs are located ([8]). For Salinity, the averaged value obtained
from the Reference stations was used for the basis as the WQO. Levels of DO and Turbidity were also assessed
for compliance with the Action and Limit Levels (see Table
B3 of Annex B for details). The monitoring results are shown in Tables
B4 and B5 of Annex B
and Figures 10 - 20 of Annex D. A total of twenty (20) monitoring stations
were sampled in January
2016 as shown in Figure 1.5.
In-situ Measurements
1.6.14
Graphical
presentation of the monitoring results (Temperature, DO, pH, Salinity and
Turbidity) is shown in Figures 10 -15 of Annex D. Analyses of results for January
2016
indicated that the levels of pH, DO and Salinity complied with the WQOs at all stations (Impact, Intermediate, Reference and
Water Sensitive Receiver stations) in January 2016 (Table B4 of Annex B; Figures 10 - 12, 14 of Annex D).
1.6.15
The levels of DO and Turbidity complied with the Action and
Limit Levels at all stations (Table
B4 of Annex B; Figures 12 and 15 of Annex D).
1.6.16
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 January
2016.
Laboratory Measurements
1.6.17
Laboratory analysis of January
2016
results indicated that concentrations of Cadmium, Lead, Silver and Mercury were
below their limit of reporting at all stations.
Arsenic, Chromium, Copper, Nickel and Zinc were detected in January 2016 samples and the concentrations were similar amongst
stations (Table B5 of Annex B; Figures
16
and 17 of Annex D).
1.6.18
For nutrients, concentrations of Total Inorganic Nitrogen
(TIN) at all stations in January 2016 exceeded the WQO
(0.5 mg/L) (Table B5 of Annex B; Figure 18 of Annex D). It should be noted
that due to effect of Pearl River, the North Western WCZ has historically
experienced higher levels of TIN ([9]).
Since TIN concentrations were recorded to be similar amongst all
stations, the exceedances of TIN WQO at all stations
are unlikely to be caused by the disposal operation at CMP 2. Ammonia Nitrogen (NH3-N) concentration was
relatively similar amongst all stations (Table B5 of Annex B; Figure 18 of Annex D). Levels of 5-day Biochemical Oxygen Demand
(BOD5) appear to be higher at Tai
Ho Bay 1 and 2 stations in January 2016 (Table B5 of Annex B; Figure 19 of Annex D).
1.6.19
Concentrations of SS complied
with the
WQO (13.5 mg/L for dry season) and the Action and Limit Levels at all stations in January 2016 (Table
B5 of Annex B; Figure 20 of Annex D).
1.6.20
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 January 2016. Detailed statistical analysis will be
presented in the Quarterly Report to investigate any spatial and temporal
trends of potential concern.
1.6.21
Water Column Profiling of CMP 2 – January 2016
1.6.22
Water Column Profiling was undertaken at a total of two sampling stations
(Upstream and Downstream stations) on 11 January
2016. The monitoring results have been assessed for
compliance with the WQOs (see Section 1.6.12 for details). Levels of DO and Turbidity were also assessed for
compliance with the Action and Limit Levels (see Table B3 of Annex B for details).
In-situ
Measurements
1.6.23
Analyses
of results for January 2016
indicated that levels of Salinity,
DO and pH complied with the WQOs at both Downstream and Upstream stations (Table B6 of Annex B). In addition, DO
and Turbidity at all stations complied with the Action and Limit Levels (Table B6 of Annex B).
Laboratory
Measurements for SS
1.6.24
Analyses
of results for December
2015 indicated that the SS levels complied with the WQO at Downstream stations. Both Upstream and Downstream stations complied with the Action and Limit Levels (Table
B6 of Annex B).
1.6.25
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 February 2016 for SB CMPs:
·
Pit Specific Sediment Chemistry of CMP 2;
·
Cumulative Impact Sediment Chemistry of CMP 2;
·
Sediment Toxicity Tests of CMP 2;
·
Routine Water Quality Monitoring of CMP 2;
·
Water Column Profiling of CMP 2;
·
Water Quality Monitoring During Capping of CMP 1;
and
·
Demersal Trawling of SB CMPs.
1.7.2
The following monitoring activities will be conducted in the next
monthly period of February 2016 for ESC CMPs:
·
Impact Water Quality Monitoring during Dredging Operations of ESC CMP V; and
·
Water Quality Monitoring During Capping 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 E.