|
Contents |
Chapter Title Page
Figures
Figure 5.1 Locations
of Water Control Zones
Figure 5.2 Locations
of Key Water Sensitive Receivers
Figure 5.3 Tentative Location of Marine Features
Figure 5.4 Tentative General Arrangement of Possible Piers
Figure 5.5 Tentative Piling Arrangement of Possible Piers
Figure 5.6 (Not
used)
Figure 5.7 Typical Drainage Pipe Outfall
Appendices
Appendix 5.1 Delft3D
Model Setup
Appendix 5.2 Predicted
Temperature Elevation at Surface Water (Dry Season
& Wet Season)
Appendix 5.3 Predicted
Depth-averaged Residual Chlorine Concentration (Dry Season & Wet Season)
This section presents an assessment of potential water quality impacts which may arise from the construction and operational stages of WKCD. Recommendations for mitigation measures have been made, where necessary, to minimise the identified water quality impacts to an acceptable level.
5.2 Water Quality Legislations, Standards and Guidelines
The criteria for evaluating water quality impacts include the following:
¡ Water Pollution Control Ordinance (WPCO) Cap. 358;
¡ Technical Memorandum on Standards for Effluents Discharged into Drainage and Sewerage Systems, Inland and Coastal Waters (TM-DSS);
¡ Water Supplies Department (WSD) Water Quality Criteria;
¡ Practice Note for Professional Persons on Construction Site Drainage (ProPECC Note PN 1/94); and
¡ District Cooling Water System (DCWS) Cooling Water Intakes Water Quality Criteria.
5.2.1 Water Pollution Control Ordinance (WPCO)
The Water Pollution Control Ordinance (WPCO) (Cap. 358) provides the statutory framework for the protection and control of water quality in Hong Kong. According to the WPCO and its subsidiary legislation, Hong Kong waters are divided into ten Water Control Zones (WCZs). Water Quality Objectives (WQOs) were established to protect the beneficial uses of water quality in WCZs. Specific WQOs are applied to each WCZ. The proposed WKCD development is located within the Victoria Harbour, Western Buffer and Eastern Buffer WCZs and their corresponding WQOs are listed in Tables 5.1, 5.2 and 5.3 respectively. The WQOs for the aforementioned WCZs had been used as the basis for assessment of water quality impacts.
Table 5.1: Water Quality Objectives for Victoria Harbour WCZ
|
Parameters |
Objectives |
Sub-Zone |
|
Offensive Odour, Tints |
Not to be present |
Whole zone |
|
Colour |
Not to exceed 50 Hazen units, due to human activity |
Inland waters |
|
Visible foam, oil scum, litter |
Not to be present |
Whole zone |
|
E. coli |
Not to exceed 1000 per 100mL, calculated as the geometric mean of the most recent 5 consecutive samples taken at intervals of between 7 and 21 days |
Inland waters |
|
Dissolved Oxygen (DO) within 2 m of the seabed |
Not less than 2
mg L-1 for 90% of the
sampling occasions during the whole year |
Marine waters |
|
Depth-averaged DO |
Not less than 4
mg L-1 for 90% of the
sampling occasions during the whole year; values should be calculated as the
annual water column average (expressed normally as the arithmetic mean of at
least 3 measurements at 1m below surface, mid depth and 1m above the seabed.
However in water of a depth of 5m of less the mean shall be that of 2
measurements – 1m below surface and 1m above seabed,
and in water of less than 3m the 1m below surface sample only shall apply.) |
Marine waters |
|
Dissolved Oxygen (DO) |
Not less than 4 mg L-1 |
Inland waters |
|
pH |
To be in the range of 6.5 - 8.5, change due to human activity not to exceed 0.2 |
Marine waters |
|
Salinity |
Change due to human activity not to exceed 10% of ambient |
Whole zone |
|
Temperature |
Change due to human activity not to exceed 2 oC |
Whole zone |
|
Suspended Solids (SS) |
Not to raise the ambient level by 30% caused by human activity |
Marine waters |
|
|
Annual median not to exceed 25 mgL-1 due to human activity |
Inland waters |
|
Unionised Ammonia (UIA) |
Annual mean not to exceed 0.021 mg L-1 as unionised form |
Whole zone |
|
Nutrients |
Shall not cause excessive algal growth |
Marine waters |
|
|
Annual mean depth-averaged inorganic nitrogen not to exceed 0.4 mg L-1 |
Marine waters |
|
BOD5 |
Not to exceed 5 mg L-1 |
Inland waters |
|
|
Not to exceed 30 mg L-1 |
Inland waters |
|
Toxic substances |
Should not attain such levels as to produce significant toxic, carcinogenic, mutagenic or teratogenic effects in humans, fish or any other aquatic organisms. |
Whole zone |
|
|
Human activity should not cause a risk to any beneficial use of the aquatic environment. |
Whole zone |
Source: Statement of Water Quality Objectives (Victoria Harbour (Phases One, Two and Three) Water Control Zone).
Table 5.2: Water Quality Objectives for the Western Buffer WCZ
|
Parameters |
Objectives |
Sub-Zone |
|
Offensive Odour, Tints |
Not to be present |
Whole zone |
|
Colour |
Not to exceed 30 Hazen units, due to human activity |
Water gathering ground subzones |
|
|
Not to exceed 50 Hazen units, due to human activity |
Other inland waters |
|
Visible foam, oil scum, litter |
Not to be present |
Whole zone |
|
E. coli |
Not to exceed 610 per 100 mL, calculated as the geometric mean of all samples collected in a calendar year |
Secondary contact recreation subzones and Fish culture subzones |
|
|
Not to exceed 180
per 100 mL, calculated as the geometric mean of all samples collected from
March to October inclusive in 1 calendar year. Samples should be taken at
least 3 times in 1 calendar month at intervals of between 3 and 14 days |
Recreation subzones |
|
|
Less than 1 per 100 mL, calculated as the geometric mean of the most recent 5 consecutive samples taken at intervals of between 7 and 21 days |
Water gathering ground subzones |
|
|
Not to exceed 1000 per 100 mL, calculated as the geometric mean of the most recent 5 consecutive samples taken at intervals of between 7 and 21 days |
Other Inland waters |
|
Depth-averaged Dissolved Oxygen (DO) |
Not less than 4
mg L-1 for 90% of the
sampling occasions during the whole year; values should be calculated as
water column average (arithmetic mean of at least 3 measurements at 1m below
surface, mid-depth and 1m above seabed) |
Marine waters except Fish culture subzones |
|
|
Not less than 5 mg L-1 for 90% of the sampling occasions during the year; values should be calculated as water column average (arithmetic mean of at least 3 measurements at 1m below surface, mid-depth and 1m above seabed) |
Fish culture subzones |
|
Dissolved Oxygen (DO) within 2 m of the seabed |
Not less than 2
mg L-1 for 90% of the
sampling occasions during the whole year |
Marine waters and Fish culture subzones |
|
Dissolved Oxygen (DO) |
Not less than 4 mg L-1 |
Water gathering ground subzones and other inland waters |
|
pH |
To be in the range of 6.5 - 8.5, change due to human activity not to exceed 0.2 |
Marine waters |
|
|
Not to exceed the range of 6.0 – 8.5 due to human activity |
Water gathering ground subzones |
|
|
Not to exceed the range of 6.0 - 9.0 due to human activity |
Other inland waters |
|
Salinity |
Change due to human activity not to exceed 10% of ambient |
Whole zone |
|
Temperature |
Change due to human activity not to exceed 2 oC |
Whole zone |
|
Suspended Solids (SS) |
Not to raise the
ambient level by 30% caused by human activity and shall not accumulate
to affect aquatic communities |
Marine waters |
|
|
Annual median not to exceed 20 mg L-1 due to human activity |
Water gathering ground subzones |
|
|
Annual median not to exceed 25 mg L-1 due to human activity |
Other inland waters |
|
Unionised ammonia (UIA) |
Annual mean not to exceed 0.021 mg L-1 as unionised form |
Whole zone |
|
Nutrients |
Shall not cause excessive algal growth |
Marine waters |
|
|
Annual mean depth-averaged inorganic nitrogen not to exceed 0.4 mg L-1 |
Marine waters |
|
5-day biochemical
oxygen demand (BOD5) |
Not to exceed 3 mg L-1 |
Water gathering ground subzones |
|
|
Not to exceed 5 mg L-1 |
Other inland waters |
|
Chemical Oxygen Demand (COD) |
Not to exceed 15 mg L-1 |
Water gathering ground subzones |
|
|
Not to exceed 30 mg L-1 |
Other inland waters |
|
Toxic substances |
Should not attain such levels as to produce significant toxic, carcinogenic, mutagenic or teratogenic effects in humans, fish or any other aquatic organisms. |
Whole zone |
|
|
Human activity should not cause a risk to any beneficial use of the aquatic environment. |
Whole zone |
Source: Statement of Water Quality Objectives (Western Buffer Water Control Zone).
Table 5.3: Water Quality Objectives for the Eastern Buffer WCZ
|
Parameters |
Objectives |
Sub-Zone |
|
Offensive Odour, Tints |
Not to be present |
Whole zone |
|
Visible foam, oil scum, litter |
Not to be present |
Whole zone |
|
Dissolved oxygen (DO) within 2m of the seabed |
Not less than 2 mg L-1 for 90% of the sampling occasions during the whole year |
Marine waters and Fish culture subzones |
|
Depth-averaged DO |
Not less than 4 mg L-1 for 90% of the sampling occasions during the whole year; values should be calculated as water column average (arithmetic mean of at least 3 measurements at 1m below surface, mid-depth and 1m above seabed) |
Marine waters excepting fish culture subzones |
|
|
Not less than 5 mg L-1 for 90% of the sampling occasions during the year; values should be calculated as water column average (arithmetic mean of at least 3 measurements at 1m below surface, mid-depth and 1m above seabed) |
Fish culture subzones |
|
|
Not less than 4 mg L-1 |
Water gathering ground subzone and other inland waters |
|
5-day biochemical oxygen demand (BOD5) |
Not to exceed 3 mg L-1 |
Water gathering ground subzones |
|
|
Not to exceed 5 mg L-1 |
Other inland waters |
|
Chemical oxygen demand (COD) |
Not to exceed 15 mg L-1 |
Water gathering ground subzones |
|
|
Not to exceed 30 mg L-1 |
Other inland waters |
|
pH |
To be in the range of 6.5 – 8.5, change due to human activity not to exceed 0.2 |
Marine waters |
|
|
To be in the range of 6.5 – 8.5 |
Water gathering ground subzones |
|
|
To be in the range of 6.0 – 9.0 |
Other inland waters |
|
Salinity |
Change due to waste discharges not to exceed 10% of ambient |
Whole zone |
|
Temperature |
Change due to waste discharges not to exceed 2 oC |
Whole zone |
|
Suspended solids (SS) |
Not to raise the ambient level by 30% caused by human activity and shall not accumulate to affect aquatic communities |
Marine waters |
|
|
Change due to human activity not to exceed 20 mg L-1 of annual median |
Water gathering ground subzones |
|
|
Change due to human activity not to exceed 25 mg L-1 of annual median |
Other inland waters |
|
Unionized ammonia (UIA) |
Annual mean not to exceed 0.021mg L-1 as unionized form |
Whole zone |
|
Nutrients |
Shall not cause excessive algal growth |
Marine waters |
|
|
Annual mean depth-averaged inorganic nitrogen not to exceed 0.4 mg L-1 |
Marine waters |
|
Toxic substances |
Should not attain such levels as to produce significant toxic, carcinogenic, mutagenic or teratogenic effects in humans, fish or any other aquatic organisms. |
Whole zone |
|
|
Human activity should not cause a risk to any beneficial use of the aquatic environment |
Whole zone |
|
E. coli |
Not exceed 610 per 100mL, calculated as the geometric mean of all samples collected in one calendar year |
Fish culture subzones |
|
|
Less than 1 per 100mL, calculated as the geometric mean of the most recent 5 consecutive samples taken at intervals of between 7 and 21 days |
Water gathering ground subzones |
|
|
Not exceed 1000 per 100mL, calculated as the geometric mean of the most recent 5 consecutive samples taken at intervals of between 7 and 21 days |
Other inland waters |
|
Colour |
Change due to human activity not to exceed 30 Hazen units |
Water gathering ground |
|
|
Change due to human activity not to exceed 50 Hazen units |
Other inland waters |
Source: Statement of
Water Quality Objectives (Eastern Buffer Water Control Zone).
Discharges of effluents are subject to control under the WPCO. The Technical Memorandum on Standards for Effluents Discharged into Drainage and Sewerage Systems, Inland and Coastal Waters (TM-DSS) sets limits for effluent discharges. Specific limits apply for different areas and are different between surface waters and sewers. The limits vary with the rate of effluent flow. Sewage from the proposed construction activities should comply with the standards for effluent discharged into foul sewers, inshore waters or marine waters of the Victoria Harbour, Western Buffer and Eastern Buffer WCZs, as shown in Tables 9a, 9b, 10a and 10b of the TM-DSS.
5.2.3
Water
Supplies Department (WSD) Water Quality Criteria
A set of water quality criteria for flushing water at seawater intakes specified by WSD as shown in Table 5.4 would be followed during construction and operation of the proposed WKCD development.
Table 5.4: WSD’s Water Quality Criteria for Flushing Water at Sea Water Intakes
|
Parameter (in mg/L unless otherwise stated) |
Target Limit |
|
Colour (HU) |
< 20 |
|
Turbidity (NTU) |
< 10 |
|
Threshold Odour Number (odour unit) |
< 100 |
|
Ammonia Nitrogen (NH3-N) |
< 1 |
|
Suspended Solids (SS) |
< 10 |
|
Dissolved Oxygen (DO) |
> 2 |
|
5-day Biochemical Oxygen Demand (BOD5) |
< 10 |
|
Synthetic Detergents |
< 5 |
|
E. coli
(no. per 100 mL) |
< 20,000 |
5.2.4
Practice
Note for Professional Persons on Construction Site Drainage (ProPECC Note PN 1/94)
A practice note for professional persons was issued by the EPD to provide guidelines for handling and disposal of construction site discharges. The Practice Note for Professional Persons on Construction Site Drainage (ProPECC Note PN 1/94) provides good practice guidelines for dealing with various types of discharge from a construction site. Practices outlined in ProPECC Note PN 1/94 should be followed as far as possible during construction to minimize the water quality impact due to construction site drainage.
5.2.5
District
Cooling Water System (DCWS) Cooling Water Intakes Water Quality Criteria
The warmed
seawater of district cooling water system (DCWS) would be discharged to the sea
through the outfalls. The discharges are called thermal discharges as the cooling water discharges that causes
thermal plumes will lead to a temperature rise in the seawater. As detailed in Table 5.1, the WQO
for the Victoria Harbour WCZ stipulated that the temperature change due to
human activity should not exceed 2oC.
Chlorine is added to the DCWS as antifouling agent or biocide to inhibit
the growth of marine organisms in the seawater intake system. However, residual
chlorine discharging to the receiving water is toxic to marine life and
potentially harmful to the environment. EPD has commissioned a study[1]
on total residual chlorine (TRC) using local species. The lowest No Observation
Effect Concentration (NOEC) value from that study was 0.02mg/L, meaning that
the total residual chlorine concentration is recommended to be no more than 0.02mg/L
at the water sensitive receivers which are exposing to the thermal
discharges with added chlorine as biocide. Nevertheless, a review of
other EIAs suggested that the TRC limit of 0.01 mg/L (for average value) could
be adopted for conservativeness and therefore TRC limit of 0.01 mg/L will be
used as the assessment criterion.
During
operation of the DCWS, the release of residual chlorine and thermal plumes in
seawater would lead to deterioration in water quality. Other than the WQOs, a
licensing system under WPCO is implemented by EPD for DCWS discharge. A
discharge license should be granted and approved by the Director of
Environmental Protection (DEP) prior to operation of DCWS. The temperature and
residual chlorine concentration should be designed at level which complies with
the stringent licensing conditions.
5.3 Assessment Area, Water Sensitive Receivers and Baseline Conditions
5.3.1 Assessment Area
Water quality impact assessment had been carried out in the Victoria Harbour, Western Buffer and Eastern Buffer Water Control Zones (WCZs) and all areas within 500m from the proposed WKCD development boundary. Locations of the water control zones are shown in Figure 5.1.
5.3.2 Water Sensitive Receivers
Key water sensitive receivers that may potentially be affected by the proposed WKCD development include:
¡ Yau Ma Tei Typhoon Shelter;
¡ WSD Flushing Water Intakes;
¡ Cooling Water Intakes; and
Locations of the key water sensitive receivers are shown in Figure 5.2.
5.3.3 Baseline Conditions
5.3.3.1 Marine Water Quality in Victoria Harbour
A summary of marine water quality data for EPD monitoring stations at Victoria Harbour (VM6 and 7), and Stonecutters Island (VM15) extracted from EPD’s publication “Marine Water Quality in Hong Kong 2010” are presented in Table 5.5. Locations of these monitoring stations are shown in Figure 5.1.
Table 5.5: Marine Water Quality at Victoria Harbour and Stonecutters Island in 2010
|
Parameter |
Monitoring Station |
||
|
|
Victoria Harbour (Central) |
Victoria Harbour (West) |
Stonecutters Island |
|
|
VM6 |
VM7 |
VM15 |
|
Temperature (oC) |
23.2 (16.6 – 27.7) |
23.0 (17.9 – 27.2) |
23.4 (16.8 – 27.6) |
|
Salinity |
31.4 (28.8 – 33.4) |
31.2 (26.1 – 33.3) |
31.0 (26.7 – 33.5) |
|
Dissolved Oxygen (mg/L) |
5.2 (3.6 – 6.5) |
5.8 (4.5 – 7.5) |
5.5 (3.9 – 6.3) |
|
Dissolved Oxygen (Bottom) (mg/L) |
4.2 (1.9 – 5.2) |
5.6 (3.4 – 7.0) |
4.8 (1.3 – 6.4) |
|
pH |
7.9 (7.6 – 8.2) |
7.9 (7.6 – 8.2) |
7.9 (7.6 – 8.2) |
|
Secchi Disc Depth (m) |
2.7 (1.0 – 5.2) |
2.7 (1.7 – 4.0) |
2.4 (1.2 – 3.6) |
|
Turbidity (NTU) |
3.1 (1.0 – 5.5) |
3.5 (1.0 – 6.6) |
3.7 (1.3 – 7.5) |
|
Suspended Solids (mg/L) |
3.5 (1.0 – 6.9) |
3.8 (1.6 – 5.6) |
4.2 (1.3 – 8.7) |
|
BOD5 (mg/L) |
1.0 (0.6 – 1.7) |
1.0 (0.5 – 1.8) |
0.9 (0.5 – 2.0) |
|
Ammonia Nitrogen (mg/L) |
0.177 (0.109 – 0.310) |
0.163 (0.090 – 0.293) |
0.199 (0.114 – 0.333) |
|
Unionised Ammonia (mg/L) |
0.006 (0.002 – 0.018) |
0.005 (0.002 – 0.014) |
0.007 (0.002 – 0.021) |
|
Nitrite Nitrogen (mg/L) |
0.031 (0.009 – 0.053) |
0.034 (0.016 – 0.078) |
0.034 (0.012 – 0.057) |
|
Nitrate Nitrogen (mg/L) |
0.141 (0.051 – 0.270) |
0.157 (0.068 – 0.347) |
0.147 (0.046 – 0.307) |
|
Total Inorganic Nitrogen (mg/L) |
0.35 (0.19 – 0.51) |
0.35 (0.20 – 0.49) |
0.38 (0.18 – 0.62) |
|
Total Kjeldahl Nitrogen (mg/L) |
0.32 (0.23 – 0.47) |
0.35 (0.25 – 0.48) |
0.34 (0.23 – 0.47) |
|
Total Nitrogen (mg/L) |
0.49 (0.30 – 0.67) |
0.55 (0.45 – 0.65) |
0.53 (0.29 – 0.73) |
|
Orthophosphate Phosphorus (mg/L) |
0.030 (0.017 – 0.048) |
0.025 (0.008 – 0.039) |
0.031 (0.016 – 0.046) |
|
Total Phosphorus (mg/L) |
0.05 (0.03 – 0.06) |
0.05 (0.04 – 0.06) |
0.05 (0.04 – 0.06) |
|
Silica (SiO2) (mg/L) |
0.91 (0.36 – 1.80) |
0.81 (0.13 – 2.13) |
0.93 (0.16 – 1.87) |
|
Chlorophyll-a (µg/L) |
3.3 (0.3 – 15.6) |
5.0 (0.4 – 13.7) |
4.1 (0.2 – 21.8) |
|
E.coli (count/100mL) |
4400 (550 – 13000) |
2800 (520 – 16000) |
1800 (430 – 5900) |
|
Faecal Coliforms (count/100mL) |
11000 (1300 – 29000) |
6100 (1000 – 28000) |
4600 (880 – 28000) |
|
Notes: Unless otherwise specified, data represented are depth-averaged (A) values calculated by taking the means of three depths: Surface (S), Mid-depth (M), Bottom (B) Data presented are annual arithmetic means the depth-averaged results except for E.coli and faecal coliforms which are annual geometric means. Data in brackets indicated the ranges. |
|||
5.3.3.2 Marine Water Quality in Yau Ma Tei Typhoon Shelter
A summary of marine water quality data for EPD monitoring stations at Yau Ma Tei Typhoon Shelter (VT10) extracted from EPD’s publication “Marine Water Quality in Hong Kong 2010” are presented in Table 5.6. Location of this monitoring station is shown in Figure 5.1.
Table 5.6: Marine Water Quality at Yau Ma Tei Typhoon Shelter in 2010
|
Parameter |
Yau Mei Tei |
|
|
VT10 |
|
Temperature (oC) |
23.6 (18.2 – 27.9) |
|
Salinity |
30.8 (29.1 – 31.8) |
|
Dissolved Oxygen (mg/L) |
4.1 (1.6 – 5.1) |
|
Dissolved Oxygen (Bottom) (mg/L) |
4.5 (3.1 – 5.6) |
|
pH |
7.7 (7.5 – 7.8) |
|
Secchi Disc Depth (m) |
1.8 (1.0 – 2.7) |
|
Turbidity (NTU) |
5.9 (1.3 – 13.6) |
|
Suspended Solids (mg/L) |
6.9 (2.8 – 15.5) |
|
BOD5 (mg/L) |
1.3 (1.0 – 1.8) |
|
Ammonia Nitrogen (mg/L) |
0.309 (0.193 – 0.450) |
|
Unionised Ammonia (mg/L) |
0.006 (0.003 – 0.011) |
|
Nitrite Nitrogen (mg/L) |
0.038 (0.023 – 0.050) |
|
Nitrate Nitrogen (mg/L) |
0.147 (0.097 – 0.200) |
|
Total Inorganic Nitrogen (mg/L) |
0.49 (0.37 – 0.64) |
|
Total Kjeldahl Nitrogen (mg/L) |
0.50 (0.41 – 0.66) |
|
Total Nitrogen (mg/L) |
0.68 (0.59 – 0.85) |
|
Orthophosphate Phosphorus (mg/L) |
0.040 (0.024 – 0.051) |
|
Total Phosphorus (mg/L) |
0.06 (0.04 – 0.07) |
|
Silica
(as SiO2) (mg/L) |
0.83 (0.12 – 1.23) |
|
Chlorophyll-a (µg/L) |
6.6 (0.8 – 21.3) |
|
E.coli (count/100mL) |
2800 (1500 – 35000) |
|
Faecal Coliforms (count/100mL) |
7400 (2700 – 71000) |
|
Notes: Unless otherwise specified, data represented are depth-averaged (A) values calculated by taking the means of three depths: Surface (S), Mid-depth (M), Bottom (B) Data presented are annual arithmetic means the depth-averaged results except for E.coli and faecal coliforms which are annual geometric means. Data in brackets indicated the ranges. |
|
5.4 Identification of Water Quality Impact
5.4.1 Construction Phase
Potential sources of water quality impact associated with the construction activities for the proposed WKCD development had been identified. These include:
¡ Construction site runoff and drainage;
¡ Modification of seawall and Construction of landing steps and possible piers/viewing platform;
¡ Barging facilities and activities;
¡ Sewage effluent from construction workforce; and
¡ General construction activities.
5.4.2 Operation Phase
Potential sources of water quality impact associated with the operation activities for the proposed WKCD development had been identified. These include:
¡ Road and surface runoff;
¡ Sewage and wastewater effluents from the proposed WKCD development;
¡ Marine piles of possible piers;
¡ Emergency effluent from optional sewage pump sump;
¡ Improvement works for New Yau Ma Tei Typhoon Shelter for odour mitigation
¡ Water reuse facilities; and
¡ Thermal/cooled water discharge from district cooling system.
5.5.1 General
Pollutants from point discharges and
non-point sources to surface water runoff, sewage from workforce and polluted
discharge generated from the proposed WKCD development and spent thermal/cooled
water discharge that could affect the quality of surface water runoff and
marine waters were identified. All identified sources of potential water
quality impact were then evaluated and their impact significance was determined.
The need for mitigation measures to reduce any identified adverse impacts in
water quality to acceptable levels was determined.
5.5.2 Thermal/cooled water discharge from district cooling system
During operation phase, seawater would be drawn into the proposed district cooling water system (DCWS) and two independent cooling systems for the 1) Freespace; and 2) the Mega Performance Venue and Exhibition Centre and the proposed hotel and retail/dining/entertainment developments on top of the Western Harbour Crossing portal (hereafter called “MPV/EC & Hotel”). The seawater, which carries heat from the cooling systems, would be discharged back to the sea through the outfalls. The Delft3D model suite, developed by Delft Hydraulics, would be used to assess the potential impact on water quality due to the operation of the proposed DCWS, and independent cooling systems for the Freespace and the MPV/EC & Hotel.
In the present study, the basis for modelling of the harbour waters is the existing, validated Western Harbour Model developed by Deltares. This model covers the relevant part of the Hong Kong waters, including the Pearl Estuary and the Dangan (Lema) Channel. A locally refined domain in the project area was inserted to obtain the higher resolution by means of a technique called “Domain Decomposition” in the model to obtain a resolution between 100m and 200m in the project area. The grid mesh was modified to generate higher resolution (about 40 m x 50 m) in the vicinity of West Kowloon. The details of the grid at the concerned area are provided in Appendix 5.1.
To ensure that an accurate coastline profile was used in the modelling, the existing model was updated with the most recently available information of proposed development from sources such as designated projects under the EIAO including the Central and Wan Chai Developments and 600m gap opening at the Kai Tak Airport Runway. The bathymetry set up was also updated based on the latest Admiralty Chart.
To simulate the thermal plume dispersion in the marine environment, the Excess Temperature Model in Delft3D-FLOW model would be employed. The model simulates the evaporation process (i.e. the heat transfer from water surface to the atmosphere at the sea/air surface). The total heat flux is proportional to the excess temperature at the surface while the rate of heat transfer depends on the temperature difference and wind speed.
The water quality model Delft3D-WAQ in the Delft3D model suite would then be employed to simulate the surplus temperature directly resulting from the discharge of seawater from the DCWS and the independent cooling systems for the Freespace and the MPV/EC & Hotel. A time history temperature elevation at each intake locations can be obtained from the model output.
In accordance with the Technical Memorandum on Standards for Effluents Discharged into Drainage and Sewerage Systems, Inland and Coastal Waters (TM-DSS), effluent discharge from the proposed cooling water systems of WKCD would not be allowed in any typhoon shelter, or within 100m of any seawater intake point including the seawater intake points of the DCWS and the independent cooling system for the Freespace and MPV/EC & Hotel.
As shown in Appendix 5.1, there are two intake points and three outfalls for the proposed DCWS, Freespace and the MPV/EC & Hotel in WKCD development. The existing intake and pump cells at WKCD will be utilized as the intakes for DCWS and Freespace. The outfall location for the proposed DCWS was proposed to be at the seawall at about 160m east of the WKCD intake while the outfall for the independent cooling system serving the Freespace will be located at about 100m west of existing MTRC Kowloon Station outfall and is at least 300m away from the closest seawater intake point. For the independent cooling system for the MPV/EC & Hotel, since the design for the intake and outfall is not available, the locations shown in the figure in Appendix 5.1 are assumed based on the 100m minimum separation from any seawater intake point requirement. Modelling would be conducted to confirm the suitability of the outfall locations and determine the potential recirculation impact.
The total cooling load demand was estimated based on the cooling load from the proposed communal facilities, residential buildings, hotels, offices and other facilities. A total of less than 20,000 Tons of refrigeration (TR) cooling load was estimated for the full development of WKCD and another less than 300 TR cooling load was required for the independent cooling system serving the Freespace[2] . On the other hand, the cooling load for the MPV/EC & Hotel was predicted to be less than 6,300 TR. To allow for full capacity of the existing pump cells, a maximum cooling load of 26,000 TR for the DCWS while based on the design cooling load of the Freespace and MPV/EC & Hotel, 1,000 TR and 8,000 TR respectively as the worst case assessment scenario for the Freespace and MPV/EC & Hotel would be simulated through the proposed intakes and outfalls as shown in Appendix 5.1.
The design excess temperature at the proposed outfalls of the DCWS and independent cooling system would be 5°C. A recirculation factor would be added to the temperatures at the intakes to address the potential short circuit issue due to recirculation of water with elevated temperature. This follows the methodology in the approved EIA Report for Express Rail Link (XRL) (EIAO Register No.: AEIAR-143/2009) and the intake temperatures would be multiplied by a factor of (1/(1-E/k), where E is the maximum of the mean temperature elevations predicted at the intakes and k is the excess temperature of cooling system (i.e. 5°C). The parameters to be adopted for the thermal plume model are summarized in Table 5.7.
Table 5.7: Summary of Parameters for Thermal Plume Model (Delft3D-FLOW)
|
Delft3D-FLOW Excess Temperature Model Parameters |
||
|
Temperature of spent cooling water (°C)* |
5°C above ambient temperature |
Dry Season Wet Season |
|
Flow rate (worst case for 26,000 TR, 1,000 TR and 8,000 TR for DCWS, Freespace and the MPV/EC & Hotel respectively) (l/s)** |
5,500 l/s, 212 l/s and 1,692 l/s |
Dry Season Wet Season |
|
Wind Speed (m/s) |
5 m/s |
Dry Season (north-east direction) and Wet Season (south-east direction) |
|
Ambient Water Temperature (°C)*** |
23°C 30°C |
Dry Season Wet Season |
Note:
* It is conservatively assumed
that the spent cooling water discharge have an excess temperature of 5°C with
reference to the background seawater temperature.
** The sea water flow rate is
estimated from the following equation: Q = H/(ρcΔT); where
Q is the sea water flow rate (m3/s);
H is the heat rejection (kW) which is estimated as the cooling load multiplied
with the heat rejection rate of 120% to 130%; ρ is the density of sea
water (kg/m3); c is the specific heat capacity of sea water
(kJ/kg/K); and ΔT is the temperature difference between sea water intake
and discharge (K).
The cooling load is 26,000TR (or
91,442 kW) and the temperature difference is 5K for the DCWS. It should be
noted that the cooling load of 26,000 TR is a rough estimate based on a heat
rejection rate of 120%. It can be estimated from the above that the sea water
flow rate is around 5.3 m3/s or 5,300 L/s (to be conservative in the model, a
sea water flow rate of 5.500 m3/s or 5,500 L/s would be simulated). Similarly,
a sea water flow rate of 212 L/s and 1,692 L/s will be adopted for simulation
for the 1,000 TR and 8,000 TR cooling load for the independent cooling systems
of the Freespace and the MPV/EC & Hotel
respectively.
*** The ambient water temperature
follows the original setting of the Western Harbour Model developed by Deltares.
For a realistic estimation of the temperature elevation, the diurnal pattern of the cooling load demand for the proposed WKCD DCWS and the independent cooling systems for the FreeSpace and the MPV/EC & Hotel were studied. Table 5.8 below showed the estimated diurnal pattern of the cooling water discharge for the proposed WKCD development. As the temperature difference for inflow and outflow of the seawater cooling system is set to 5K and only the flow rate will vary with time. The flow rate input into the thermal model at any time of a day follows this formula:
Flow Rate at Hr T = 5,500 l/s x (% full cooling load at Hr T shown in Table 5.8)
On the other hand, the flow of the proposed seawater cooling system of XRL follows its own diurnal pattern as mentioned in Section 11.57 of the XRL EIA Report. The hourly diurnal flow of XRL seawater cooling system adopted in XRL EIA Report was input into the model for this project.
Table 5.8: Diurnal pattern of cooling water discharge for proposed WKCD DCWS and the independent cooling systems
|
Hours |
% of full cooling load for the proposed DCWS* |
% of full cooling load for Freespace^ |
% of full cooling load for MPV/EC & Hotel^ |
|
00:00 – 02:00 |
62 |
70 |
71 |
|
02:00 – 04:00 |
51 |
40 |
55 |
|
04:00 – 06:00 |
51 |
40 |
52 |
|
06:00 – 08:00 |
58 |
50 |
58 |
|
08:00 – 10:00 |
62 |
50 |
62 |
|
10:00 – 12:00 |
71 |
60 |
70 |
|
12:00 – 14:00 |
74 |
65 |
74 |
|
14:00 – 16:00 |
78 |
75 |
79 |
|
16:00 – 18:00 |
84 |
85 |
82 |
|
18:00 – 20:00 |
84 |
100 |
88 |
|
20:00 – 22:00 |
79 |
100 |
87 |
|
22:00 – 00:00 |
74 |
100 |
88 |
Note: *The %full cooling load at
different times of the day are estimated by summing up the anticipated cooling
demand of recreational, residential, commercial, hotel, retails uses at
different times of the day in WKCD. Full cooling load demand was not predicted
to happen as the cooling requirement varies for different types of buildings at
different hours of the day.
^The design cooling load profile
for CACF is adopted for the Freespace; whilst a
composite pattern derived from design cooling load profile for CACF, hotel,
office, retail, dinning and entertainment is adopted
for the MPV/EC & Hotel.
The existing and proposed seawater cooling systems near the proposed WKCD development have been considered. From the approved EIA Report for Express Rail Link (XRL) (EIAO Register No.: AEIAR-143/2009), the locations, flow rates and the typical diurnal flow pattern for the XRL intake and outfall were referenced. Information on other private systems was sought from property operators. Assumptions on the flow rates were made from the available information where appropriate. The cooling water discharge of the proposed WKCD development and other systems would be modelled to assess the cumulative impact. The approximate distances of these intakes and outfall from the WKCD DCWS proposed outfall (excluding the outfall of the independent cooling systems) were presented in Table 5.9 and their locations are shown in Appendix 5.1.
Table 5.9: Approximate distances of existing cooling water intakes and outfalls from the WKCD DCWS proposed Outfall
|
Existing cooling systems |
Distances to proposed WKCD DCWS Outfall (m) |
|
|
|
Intake |
Outfall |
|
Ocean Centre |
740 |
830 |
|
Harbour City |
700 |
630 |
|
Ocean Terminal |
830 |
830 |
|
West Kowloon Terminus (under construction) |
370 |
270 |
|
China H.K. City |
360 |
550 |
|
Elements |
190 |
460 |
|
MTRC Kowloon Station |
330 |
510 |
Due to the existing site constraints including the location of the existing seawater and cooling water intakes, the outfall of the proposed WKCD DCWS is limited to the location shown in Appendix 5.1.
5.5.2.3 Residual Chlorine
The water quality model Delft3D-WAQ in the Delft3D model suite was employed for assessing the residual chlorine discharged from the cooling water. Other anti-fouling chemical agent (e.g. C-treat-6) would not be used at the proposed DCWS. With confirmation on the engineering design, a residual chlorine concentration of 0.2 mg/L has been adopted for the proposed WKCD development.
The discharge of residual chlorine would be represented by a decayable tracer in the WAQ model. As the WAQ model was coupled to the FLOW model with a “communication file” between the two models, diffusion and dispersion of the chlorine would be based on the flow determined in the hydrodynamic model. Each flow simulation would cover a complete spring-neap tidal cycle (approximately 15 days).
Following the approved XRL EIA Report, the
T90 factor (time to decay by 90%) adopted in the approved XRL EIA Report for
the project Tai Po Sewage Treatment Works
Stage V (EIAO Register No.:
AEIAR-081/2004) is the most conservative value among the
past EIA studies. Therefore the chlorine decay value (T90 = 8289s) used under
these two studies would be adopted. Conversion of the unit to suit the
parameter in the WAQ model was done and the calculated decay rate was 24/d.
Summary of parameters to be used in the Delft3D-WAQ model is presented in Table 5.10.
Moreover, due to the high decay rate of
chlorine in marine waters, the ambient chlorine level is assumed to be
negligible. As no background chlorine would be included in the water quality
model, only the elevation of residual chlorine would be evaluated.
Table 5.10: Summary of Parameters for Modelling of Residual Chlorine (Delft3D-WAQ)
|
Particle Track Model Parameters |
||
|
Vertical Dispersion Coefficient (m2/s)* |
5 x 10-3 1 x 10-5 |
Dry Season Wet Season |
|
Residual Chlorine of seawater cooling discharge (mg/L) |
0.2 |
Dry Season Wet Season |
|
Decay rate (/d) |
24 |
Dry Season Wet Season |
|
Flow Rate (m3/s) |
Equivalent to flow rates in the thermal model |
Dry Season Wet Season |
Note:
*Values presented are commonly adopted and in line in
the XRL EIA.
The impacts from other existing seawater
cooling systems near the proposed WKCD development would be included in the
model to assess the cumulative impact, similar to the thermal plume modelling.
5.6 Prediction and Evaluation of the Water Quality Impact
5.6.1 Construction Phase
5.6.1.1 Construction site runoff and drainage
Runoff
from the surface construction works areas may contain increased loads of
sediments, other suspended solids (SS) and contaminants. Potential sources of
pollution from site drainage include:
¡ Runoff
from and erosion from site surfaces, drainage channels, earth working areas and
stockpiles
¡ Release
of any bentonite slurries, concrete washings and
other grouting materials with construction run-off and storm water
¡ Wash
water from dust suppression sprays and wheel wash facilities
¡ Fuel,
oil, solvents and lubricants from maintenance of construction vehicles and
mechanical equipment
Sediment
laden runoff particularly from works areas subjected to excavation or earth
works, if uncontrolled, may carry pollutants (adsorbed onto the particle
surfaces) into any nearby storm water drains. Bentonite
and chemical grouting may be required for diaphragm walling works and as a
result may pollute surface runoff.
As
a good site practice, mitigation measures should be implemented to control
construction site runoff and drainage from the works areas, and to prevent
runoff and drainage water with high levels of SS from entering any nearby storm
water drains. With the implementation of adequate construction site drainage and
provision of sediment removal facilities, unacceptable water quality impacts
are not anticipated. The construction phase discharge would be collected by the
temporary drainage system installed by the Contractor and then treated or desilted on-site before discharge to storm water drains.
The Contractor would be required to obtain a license from EPD under the WPCO for
discharge to the public drainage system.
5.6.1.2 Modification of seawall and Construction of landing steps and possible piers/viewing platform
The tentative location of marine features including
landing steps, possible piers and viewing platform for the proposed WKCD
development are shown in Figure 5.3.
Construction of cooling water discharges/outfalls to the south and west of the proposed WKCD development would involve minor seawall modification. Typical cross section of drainage pipe outfall is shown in Figure 5.7. Detailed design of the cooling water discharges/outfalls would be available at the detailed design stage. In general, the construction sequence is that a temporary cofferdam in the form of sheet-pile wall outside the cooling water discharge/outfall would be constructed prior to the construction of the cooling water discharge/outfall. Excavation of fill material from the existing seawall above the existing seabed would be carried out. The outfall pipe would be positioned in temporary open cuts in the existing seawall well above the existing seabed. Once the outfall pipe have been installed and checked for alignment, the seawall would be reinstated by backfilling to match the existing condition. Dredging operation would not be anticipated and dredging of marine sediment would not be required for the construction of cooling water discharges/outfalls. Nevertheless, this might still results in small amount of suspended solids released from the surface of the seawall. Silt curtain should be deployed to completely enclose the seawall modification for construction of the cooling water discharges/outfalls.
Construction of landing steps at the south and south west of the proposed WKCD development would also involve minor seawall modification. Detailed design of the landing steps would be available at the detailed design stage. In general, the landing steps are anticipated to be founded on piles. The pile foundation would be fixed into the seabed either by driving or drilling. Part of the rockfill of the seawall where the landing steps are located would be removed. Precast steps would be installed to form the landing steps. The seawall would be reinstated by backfill with rocks and gravels to match the existing condition. The proposed landing steps are designed for public amenity purpose and as an integrated part of the waterfront promenade and WKCD landscaped space. They would not be designed to serve any marine traffic. Formation of basins for marine access is therefore not anticipated. No dredging of marine sediment would be required. Dredging operation would not be anticipated for the construction of landing steps. Nevertheless, this might still results in small amount of suspended solids released from the surface of the seawall. Silt curtain should be deployed to completely enclose the seawall modification and construction of the landing steps.
By adopting this preventive measure, it is considered
that the seawall modification for construction
of the cooling water discharge/outfalls and landing steps would not cause adverse impact to the aquatic life and
environment.
Installation of marine piles would be required for the possible piers. The tentative general and piling arrangement of the possible pier are shown in Figures 5.4 and 5.5 respectively. Detailed design of the possible piers would be available at the detailed design stage. In general, the footing of the piles would mainly be in place on the seabed adjacent to the under-water seawall. In order to support the deck of the possible pier and provide sufficient space for visitors for boarding, there are a total of about 26 piles (each with a diameter of about 0.7m diameter) to form an array with at least about 2m gap between each pile. The pier deck has its length of about 50m and width of about 6 to 7m.The installation of the piles would include driving the piles mainly into the seabed adjacent to the under-water seawall. Part of the rockfill of the seawall where part of the possible piers are located would be removed. Socked H-piles are installed by inserting H-piles into pre-bored holes sunk into bedrock and subsequently grouting the holes with cementitious materials. A temporary casing passing through the soil layer would be provided in the pre-boring process to prevent collapse of the seabed and sediment from falling into the pre-bored hole. Conventional drilling system should be employed to drill through all materials above the rock head level. The seawall would be reinstated by backfill with rocks and gravels to match the existing condition. Excavation of marine sediment is therefore not expected. As the possible piers are proposed for visitors or leisure activities, installation of piles with large diameters are not necessary. Formation of basins for marine access is also not anticipated as the water depth to the south and west of the proposed WKCD development is at least 7m. No dredging of marine sediment is expected. Nevertheless, this might still results in small amount of suspended solids released from the surface of the seabed. Silt curtain should be deployed to completely enclose the pile installation works. By adopting this preventive measure, the impacts of the marine pile installation works on water quality is expected to be minimal.
The viewing platform is an extension of the waterfront promenade, possibly composed of cantilever structure on top seabed and foreshore only. Therefore, the construction of viewing platform is not expected to cause adverse impact on water quality.
5.6.1.3 Barging facilities and activities
Barging point facilities of the Hong Kong Section of Guangzhou - Shenzhen - Hong Kong Express Rail Link project at the West Kowloon seafront would be used for handling of spoil generated from excavation works for the proposed WKCD development. Barging activities might cause adverse impact on water quality if not handled properly. Mitigation measures are recommended to control any pollutant discharge into the sea due to barging activities. Impact due to barging activities is expected to be insignificant provided all recommended mitigation measures are properly implemented.
5.6.1.4 Sewage effluent from construction workforce
Domestic
sewage would be generated from the workforce during construction phase. However,
portable chemical toilets should be installed within the construction site. The
Contractor have the responsibility to ensure that chemical toilets are used and
properly maintained, and that licensed Contractors are employed to collect and
dispose of the waste off-site at approved locations. Therefore, water quality
impact is not anticipated.
5.6.1.5 General construction activities
On-site
construction activities may result in water pollution from the following:
¡ Uncontrolled
discharge of debris and rubbish such as packaging, construction materials and
refuse; and
¡ Spillages
of liquids stored on-site, such as oil, diesel and solvents etc.
Good
construction and site management practices should be observed to ensure that
litter, fuels and solvents do not enter the public drainage system.
5.6.2 Operation Phase
5.6.2.1 Road and surface runoff
Surface runoff from the local road
network proposed under the WKCD development may be contaminated by oils leaked
from passing vehicles. It is considered that impacts upon water quality
would be minimal provided that the proposed WKCD development and associated
local road network are designed with adequate drainage systems and appropriate
oil interceptors, as required in accordance with Highways Department Guidance Notes RD/GN/035 – Road Pavement Drainage
Design.
5.6.2.2 Sewage and wastewater effluents from the proposed WKCD development
The
Development Plan for WKCD proposes a number of Core Art and Cultural Facilities
(CACF) combined with commercial, catering and retail facilities. A park is also
proposed to be located at the south western portion of the WKCD. Under the
development plan, the total pollution of WKCD is about 120,000.
Sewage
and wastewater effluents generated from the proposed WKCD development would be
connected to the proposed foul sewerage system as detailed in Section 6.
Hydraulic
assessment had been conducted and the results had concluded that adverse sewerage
impact to the existing 1350mm trunk sewer, the sewer along Austin Road West and
Lin Cheung Road and the sewer along Canton Road in which the sewage form the
proposed WKCD development will be discharged to are
not predicted. The local sewerage network should therefore have sufficient
capacity to cater for the sewage flow generated from the proposed WKCD
development.
Recommendations
for the design, operation and maintenance for the sewerage system are detailed
in Section 6.
5.6.2.3 Marine piles of possible piers
The presence of the marine piles would create forces on the tidal flow which result in energy loss of the flow and eventually impact the flushing capacity within the vicinity of the possible piers. In view of the orientation of the piles and their sizes as indicated in Figures 5.4 and 5.5, potential impacts of the provision of the marine piles on flushing capacity in the vicinity of the possible piers is expected to be insignificant.
5.6.2.4 Emergency effluent from optional sewage pump sump
The optional sewage pump sump would be located at the basement of the Freespace and the proposed installed capacity is estimated to be approximately 580 m3 per day.
Potential water quality impact associated with the optional sewage pump sump include occasional overflow of sewage effluent during storm event under normal operation and emergency sewage effluent discharge as a consequence of pump failure or interruption of power supply. A two hour emergency storage capacity would be provided within the optional sewage pump sump according to EPD‘s Environmental Guidance Note for Sewage Pumping Stations which is NOT a Designated Proejct. Pump sets would be provided with 100% standby of the operational capacity. Emergency over pumping utilising temporary pumps and emergency power supply to convey sewage to the gravity sewerage system would be arranged in the event all pumps duty and standby were to fail. Provision of standby pumps and dual power supply with sufficient capacity (100% standby of the operational capacity) would mean there would not be occurrence of such effluent discharge. No emergency effluent overflow or bypass is to be provided from the optional sewage pump sump located within the deep basement of the Freespace. Water quality impact as a result of overflow of sewage effluent is therefore not anticipated.
With the implementation of the aforesaid design measures, adverse water quality impact associated with emergency effluent bypass from the optional sewage pump sump is not anticipated.
5.6.2.5 Improvement works for New Yau Ma Tei Typhoon Shelter for Odour Mitigation
It has been ascertained that malodour emissions from New Yau Ma Tei Typhoon Shelter (NYMTTS) are localized at the areas in the vicinity of outfalls from the Cherry Street and Jordon Road Box Culverts and are mainly due to effluent discharges from these two Box Culverts. The most effective way to mitigate the malodour emissions is to stop or prevent the effluent discharges from entering the NYMTTS via the Cherry Street and Jordon Road Box Culverts. To achieve this, the short term measures of rectifying any identified expedient connections and desilting of sediments at the two Box Culverts have been in-progress by the relevant government departments. In addition, relevant dry weather flow interceptors (DWFI) improvement measures including improvement in interception of effluent discharge were proposed for NYMTTS. In order to help mitigate the odour emission from NYMTTS, it has been recommended to implement the project to construct a new DWFI at the outlet of the Cherry Street Box Culvert as well as the proposed upgrading works for the existing DWFIs upstream of the Cherry Street Box Culvert and/or the Jordon Road Box Culvert so that the malodour emissions due to effluent discharge from the Box Culverts could be effectively reduced. Details of these improvement measures are given in Section 3.7.3.1.
5.6.2.6 Water reuse facilities
Options to be considered for the optional water reuse facilities include green building initiatives such as rainwater harvesting and reuse of condensate from air conditioning systems. Water collection and treatment system would be installed for reuse of the reclaimed water which is being considered for potential uses such as irrigation. The Architectural Services Department (ASD) has guidelines for design of rainwater recycling installations, which recommend standards for recycled rainwater quality as shown in Table 5.11.
Table 5.11: Recommended Standard of Recycled Rainwater
Quality
|
Parameter |
Unit |
Recommended Water Quality Standards |
|
E. Coli |
cfu/100ml |
Non Detectable |
|
Total Residual Chlorine |
mg/L |
≥ 1 exiting treatment system; ≥ 0.2 at user end |
|
Dissolved Oxygen in Reclaimed Water |
mg/L |
≥ 2 |
|
Total Suspended Solid (TSS) |
mg/L |
≤ 5 |
|
Colour |
Hazen Unit |
≤ 20 |
|
Turbidity |
NTU |
≤ 5 |
|
pH |
/ |
6 - 9 |
|
Threshold Odour Number (TON) |
/ |
≤ 100 |
|
5-day Biochemical Oxygen Demand (BOD5) |
mg/L |
≤ 10 |
|
Ammoniacal Nitrogen |
mg/L as N |
≤ 1 |
|
Synthetic Detergents |
mg/L |
≤ 5 |
Source: Water Supplies Department, The
Government of the HKSAR.
Note:
1.
Apart from total
residual chlorine which ahs been specified, the water
quality standards for all parameters shall be applied at the point-of-use of
the system.
2.
Where recycled
water is treated for immediate usage, the level of total residual chlorine may
be lower than the one specified in this table.
3.
Immediate usage
means the collected grey water / rainwater is drawn into the treatment process
immediate before a particular round of usage and the treated water will be
depleted after that round of usage is completed.
Rainwater can be directly harvested from rooftop installations. It may contain trace amounts of particulates, but is otherwise considered to be a safe and clean source of water for non-potable use. Provided that the rainwater harvesting installation is well maintained, no adverse impact is anticipated from reuse of rainwater for irrigation. Condensate from air conditioning can be collected as part of the system and delivered to a disinfection unit to remove microorganisms prior to reuse for irrigation. Provided that the disinfection system is adequately designed and implemented, no adverse impact is anticipated from reuse of condensate for irrigation. Demand for reclaimed water is significant and discharge of surplus reclaimed water is not anticipated. Water quality impact as a result of discharge of surplus reclaimed water is therefore not anticipated. Discharge of surplus reclaimed water, if deemed necessary, would be required to comply with requirements specified in the WPCO.
5.6.2.7 Thermal/cooled water discharge from district cooling system
In accordance with the methodology as presented in Section 5.5.2.2, the thermal plume model was run for the proposed cooling load demand for the project with other existing cooling water discharges.
Temperature Elevation
In the WQO, it was stipulated that the temperature increase in the water column due to human activity should not exceed 2°C. Since the intakes of the cooling water system will be located at around -3.15 mPD, the temperature elevations near the mid-depth of the water column are taken from the model. The summary of results of the aforesaid scenario is shown in Table 5.12. The temperature elevations at the surface level of the water column at different tidal conditions in dry and wet seasons are shown in the plots in Appendix 5.2.
Table 5.12: Temperature elevations at cooling water
intakes
|
Water sensitive receivers |
Temperature elevation at cooling water intakes in ◦C |
|||
|
|
Dry season |
Wet season |
||
|
|
Mean |
90 percentile |
Mean |
90 percentile |
|
MTRC Kowloon Station (C1) |
0.17 |
0.29 |
0.47 |
1.05 |
|
West Kowloon Terminus (under construction) (C2) |
0.59 |
0.75 |
0.85 |
1.48 |
|
China H.K. City (C3) |
0.38 |
0.50 |
0.48 |
0.73 |
|
Harbour City (C4) |
0.21 |
0.27 |
0.22 |
0.37 |
|
Ocean Centre (C5) |
0.30 |
0.45 |
0.55 |
1.07 |
|
Ocean Terminal (C6) |
0.15 |
0.25 |
0.12 |
0.22 |
|
The Elements (C7) |
0.19 |
0.38 |
0.69 |
1.54 |
|
WSD Intake (WSD1) |
0.08 |
0.11 |
0.04 |
0.09 |
|
Existing Intake for WKCD DCWS (including Freespace) |
0.20 |
0.38 |
0.71 |
1.55 |
|
Proposed Intake of Independent Cooling System for MPV/EC & Hotel |
0.10 |
|||