Agreement No. CE 63/2016 (EP)

Environmental Monitoring and Audit
for Disposal Facility to the East of Sha Chau (2017-2020) - Investigation

MONTHLY EM&A REPORT FOR March 2018

1.1                                        Background

1.1.1                          The Civil Engineering and Development Department (CEDD) is managing a number of marine disposal facilities in Hong Kong waters, including the Contaminated Mud Pits (CMPs) to the South of The Brothers (SB) and to the East of Sha Chau (ESC) for the disposal of contaminated sediment, and open-sea disposal grounds located to the South of Cheung Chau (SCC), East of Tung Lung Chau (ETLC) and East of Ninepins (ENP) for the disposal of uncontaminated sediment.  Two Environmental Permits (EPs), EP-312/2008/A and EP-427/2011/A, were issued by the Environmental Protection Department (EPD) to the CEDD, the Permit Holder, on 28 November 2008 and 23 December 2011 for the Dredging, Management and Capping of Contaminated Sediment Disposal Facilities at ESC CMP V and SB CMPs, respectively.

1.1.2                          Under the requirements of the two EPs for ESC CMP V and SB CMPs, EM&A programmes which encompass water and sediment chemistry, fisheries assessment, tissue and whole body analysis, sediment toxicity and benthic recolonisation studies as set out in the EM&A Manuals are required to be implemented.  EM&A programmes have been continuously carried out during the operation of the CMPs at ESC and SB.  A review of the collection and analysis of such environmental data from the monitoring programme demonstrated that there had not been any adverse environmental impacts resulting from disposal activities ([1]) ([2]).  The current programme will assess the impacts resulting from dredging, disposal and capping operations of CMP V as well as capping operations of SB CMPs.

1.1.3                          The present EM&A programme under Agreement No. CE 63/2016 (EP) covers the dredging, disposal and capping operations of the ESC CMP V as well as the capping operations of the SB CMPs (see Annex A for the EM&A programme).  Detailed works schedule for ESC CMP V and SB CMPs is shown in Figure 1.1.  In March 2018, the following work was being undertaken:

·     Disposal of contaminated mud at ESC CMP Vd.

Figure 1.1      Works Schedule for ESC CMP V and SB CMPs

1.2                                        Reporting Period

1.2.1                          This Monthly EM&A Report for March 2018 covers the EM&A activities for the reporting month of March 2018.

1.3                                        Details of Sampling and Laboratory Testing Activities

1.3.1                          The following monitoring activities were undertaken for ESC CMP V in March 2018:

·     Water Column Profiling of ESC CMP Vd; and

·     Pit Specific Sediment Chemistry of ESC CMP Vd.

1.3.2                          No monitoring activities were undertaken for SB CMP in March 2018.

1.4                                        Details of Outstanding Sampling and/or Analysis

1.4.1                          No outstanding sampling remained for March 2018. 

1.5                                        Brief Discussion of the Monitoring Results for ESC CMP V

1.5.1                                 Brief discussion of the monitoring results of the following activities for ESC CMP V is presented in this Monthly EM&A Report for March 2018:

·     Water Column Profiling of ESC CMP Vd in March 2018;

·     Pit Specific Sediment Chemistry of ESC CMP Vd in February and March 2018; and

·     Cumulative Impact Sediment Chemistry for ESC CMP V in February 2018.

1.5.2                                 Water Column Profiling of ESC CMP Vd – March 2018

1.5.3                          Water Column Profiling was undertaken at a total of two sampling stations (Upstream and Downstream stations) on 6 March 2018.  The monitoring results 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 2007 - 2016 from stations in the Northwestern Water Control Zone (WCZ), where the ESC CMPs are located ([3]).  For Salinity, the averaged value obtained from the Reference (Upstream) station 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 B1 of Annex B for details). 

In-situ Measurements

1.5.4                          Analyses of results for March 2018 indicated that levels of DO, Salinity and pH complied with the WQOs at both Downstream and Upstream stations (Table B2 of Annex B).  In addition, levels of DO and Turbidity at all stations complied with the Action and Limit Levels (Tables B1 and B2 of Annex B). 

Laboratory Measurements for Suspended Solids (SS)

1.5.5                          Analyses of results for March 2018 indicated that the SS levels complied with the WQO and the Action and Limit Levels at both Upstream and Downstream stations (Tables B1 and B2 of Annex B). 

1.5.6                          Overall, the monitoring results indicated that the mud disposal operation at ESC CMP Vd did not appear to cause any deterioration in water quality during this reporting period.

1.5.7                          Pit Specific Sediment Chemistry of ESC CMP Vd – February and March 2018

1.5.8               Monitoring locations for Pit Specific Sediment Chemistry for ESC CMP Vd are shown in Figure 1.2.  A total of six (6) monitoring stations were sampled in February and March 2018. 

1.5.9               The concentrations of all inorganic contaminants were lower than the Lower Chemical Exceedance Level (LCEL) at most stations in February and March 2018, except the exceedance of LCEL for Arsenic at Active Pit station ESC-NPAB in March 2018 (Figures 1, 2, 5 and 6 of Annex C). 

1.5.10             Whilst the average concentration of Arsenic in the Earth’s crust is generally ~2mg/kg, significantly higher Arsenic concentrations (median = 14 mg/kg) have been recorded in Hong Kong’s onshore sediments ([4]).  It is presumed that the natural concentrations of Arsenic are similar in onshore and offshore sediments ([5]), and relatively high Arsenic levels may thus occur throughout Hong Kong.  Therefore, the LCEL exceedances of Arsenic are unlikely to be caused by the disposal operations at ESC CMP Vd but rather as a result of naturally occurring deposits.

1.5.11             For organic contaminants, the concentrations of Total Organic Carbon (TOC) were generally similar in February and March 2018 (Figures 3 and 7 of Annex C).  The concentration of Tributyltin (TBT) was generally higher at Active-Pit stations ESC-NPAB and ESC-NPAA in February and March 2018, respectively (Figure 4 and 8 of Annex C).  Low and High Molecular Weight Polycyclic Aromatic Hydrocarbons (PAHs), Total Polychlorinated Biphenyls (PCBs), Total dichloro-diphenyl-trichloroethane (DDT) and 4,4’-dichlorodiphenyldichloroethylene (DDE) concentrations were below the limit of reporting at all stations in February and March 2018.

1.5.12              Overall, there is no evidence indicating any unacceptable environmental impacts to sediment quality as a result of the contaminated mud disposal operations at ESC CMP Vd in February and March 2018.  Statistical analysis will be undertaken and presented in the corresponding quarterly report to investigate whether there are any unacceptable impacts in the area caused by the contaminated mud disposal. 

1.5.13                       Cumulative Impact Sediment Chemistry of ESC CMP VFebruary 2018

1.5.14                       Monitoring locations for Cumulative Impact Sediment Chemistry for ESC CMP V are shown in Figure 1.3.  A total of nine (9) monitoring stations were sampled in February 2018. 

1.5.15                       Analyses of results for the Cumulative Impact Sediment Chemistry Monitoring indicated that the concentrations of most inorganic contaminants were below the LCEL at all stations in February 2018, except Arsenic exceeded the LCEL at Mid Field stations ESC-RMA and ESC-RMB as well as the Far Field stations ESC-RFA and ESC-RFB (Figures 9 and 10 of Annex C).

1.5.16                       As discussed in Section 1.5.10, the natural concentrations of Arsenic are relatively high in Hong Kong.  Therefore, the LCEL exceedances of Arsenic are unlikely to be caused by the disposal operations at ESC CMP Vd but rather as a result of naturally occurring deposits.

1.5.17                        For organic contaminants, the concentrations of TOC were generally similar in February 2018 with lower concentrations recorded at Capped Pit stations ESC-RCA and ESC-RCB (Figure 11 of Annex C).  The concentrations of TBT were recorded to be higher at Ma Wan station (Figure 12 of Annex C).  Low and High Molecular Weight PAHs, PCBs, DDT and DDE concentrations were generally recorded below the limit of reporting at all stations, except concentrations of High Molecular Weight PAHs was higher than the limit of reporting at Capped Pit station ESC-RCA (Figure 13 of Annex C).

1.5.18                        Overall, there is no evidence indicating any unacceptable environmental impacts to sediment quality as a result of the contaminated mud disposal operations at ESC CMP Vd in February 2018.  Statistical analysis will be undertaken and presented in the corresponding quarterly report to investigate whether there are any unacceptable impacts in the area caused by the contaminated mud disposal.

1.6                                        Activities Scheduled for the Next Month

1.6.1                          The following monitoring activities will be conducted in the next monthly period of April 2018 for ESC CMP V (see Annex A for the sampling schedule):

·     Water Column Profiling of ESC CMP Vd;

·     Routine Water Quality Monitoring of ESC CMP V; and

·     Pit Specific Sediment Chemistry of ESC CMP Vd.

1.6.2                          No monitoring activities are scheduled to be undertaken for SB CMPs in April 2018.

1.7                                        Study Programme

1.7.1                          A summary of the Study Programme is presented in Annex D.


 


([1])    ERM (2013)  Final Report.  Submitted under Agreement No. CE 4/2009 (EP) Environmental Monitoring and Audit for Contaminated Mud Pit at East Sha Chau.  For CEDD.

([2])     ERM (2017)  Final Report.  Submitted under 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).  For CEDD.

([3])   http://epic.epd.gov.hk/EPICRIVER/marine/?lang=en

([4])     Sewell RJ (1999) Geochemical Atlas of Hong Kong. Geotechnical Engineering Office, Government of the Hong Kong Special Administrative Region

([5])     Whiteside PGD (2000) Natural geochemistry and contamination of marine sediments in Hong Kong. In: The Urban Geology of Hong Kong (ed Page A & Reels SJ). Geological Society of Hong Kong Bulletin No. 6, p109-121