7                                            SEWERAGE AND SEWAGE TREATMENT IMPLICATIONS

7.1                                      Introduction

This Section outlines the existing sewerage arrangements in the vicinity of the Development Site and examines the available capacity of the existing sewerage system.  If there is no existing sewerage system in the vicinity to serve the Site, the technical feasibility of providing a sewage disposal scheme will be assessed.  This Sewerage and Sewage Treatment Implications Assessment (SSTIA) demonstrates that the proposed development is viable in terms of its impact on the sewerage system.

7.2                                      Relevant Legislative Requirements

The Development Site is currently on highland without any development.  It is accessible by Sha Lo Tung Road.  A description of how the Site is intended to be developed is presented in Section 3.

According to Section 11.1 of the Technical Memorandum of Standards for Effluents Discharged into Drainage and Sewerage Systems, Inland and Coastal Waters published by Environmental Protection Department, no new effluents are allowed in the following areas, regardless of the standards of the effluents:

1.         Within 100 m of the boundaries of a gazetted beach in any direction, including rivers, streams and storm water drains;

2.         Within 200 m of the seaward boundaries of a marine fish culture zone or a site of special scientific interest, and within 100 m of the landward boundaries;

3.         In any typhoon shelter;

4.         In any marine park; and

5.         Within 100 m of a seawater intake point.

The Site falls in the vicinity of two SSSIs and no treated effluents are allowed to be discharged within 100 m of the landward boundaries of the SSSIs. 

7.3                                      Assessment Methodology

The SSTIA was undertaken in accordance with the criteria and guidelines for evaluating and assessing impacts on the downstream public sewerage, sewage treatment and disposal facilities as states in section 6.5 in Annex 14 of the Technical Memorandum on Environmental Impact Assessment process (Environmental Impact Assessment Ordinance, Cap. 499, S.16).  The following methodology was adopted for this SSTIA:

·            Investigation of the existing and planned sewerage facilities in the area of the development site;

·            Calculation of the sewage flow generated from the proposed development; and

·            Investigation of three sewerage disposal options for the development site.

7.4                                      Existing Sewerage Facilities and Planned Sewerage in the Area

The Development Site is within an area where no public sewerage connection is available.  There is only a pubic toilet located at the end of Sha Lo Tung Road.  The effluent from the public toilet is treated by the soakaway method.

The nearby existing sewerage system is a sewer network to the south of Ting Kok Road.  It includes sewers and a pumping station.  The sewers collect the sewage from Fung Yuen, about 700 m to the south of the Development Site, and feed it into the pumping station located at the junction of Fung Yuen Road and Ting Kok Road.  The sewage is pumped across Ting Kok Road and discharged into the public sewer network at Tai Po Industrial Estate at a manhole located at the junction of Dai Fat Street and Ting Kok Road.

The public sewer network will carry the sewage to Tai Po Sewage Treatment Works (STW) located at the eastern part of the Tai Po Industrial Estate.  This STW provides primary and secondary treatment.  The existing sewerage network is shown in Figure 7.1.

7.5                                      Estimated Sewerage Flow

The quantity of wastewater generated by the proposed development is calculated based on Appendix III of Guidelines for Estimating Sewage Flows for Sewage Infrastructure Planning (the Guidelines) ([1]).  The sewage generated from the Nature Interpretation Centre, Multi-Cultural Education Retreat cum Columbarium is calculated on the assumption of a maximum of 200 visitors per day.  The waste water generated during special festivals such as Ching Ming or Chung Yeung, when visitor numbers will be much higher, is discussed in Section 7.7. 

The calculations of Average Dry Weather Flow (ADWF) are shown as follow:

Maximum No. of Visitors =  200

Global unit flow rate = 0.080 m3/day  (ref. 4(d) of Appendix III of the Guidelines)

Maximum ADWF =  200 x 0.080 m3/day  =  16.0 m3/day  =  0.185 l/s

The visitors will remain on the Site during the open hours from 9:00am to 5:00pm.  The sewage generated by the visitors will be the water for flushing and washing hands only.  Since the behaviour of visitors in terms of sewage generation is similar to the behaviour of employees, a unit flow rate of 0.080 m3/day according to Clause 4(d) of Appendix III of the Guidelines is used.

As there is no statutory requirement or guideline for the assessment of sanitary fitments for religious places, the assessment of sanitary fitments for cinemas as required in PNAP 297 is referenced.  At least 10 female W.C., 4 male W.C. and 7 male urinals are assumed to be provided in the Multi-Cultural Education Retreat and Columbarium for public use during the operation phase.  The toilet facilities to be provided in the Site are adequate to cater for a maximum of 200 visitors (including visitors to Nature Interpretation Centre but no visitors or staffs of the Nature Interpretation Centre would stay overnight).

On a normal day, not more than 30 occupants will be in the Multi-Cultural Education Retreat cum Columbarium & other facilities stay overnight.  The calculations of Average Dry Weather Flow (ADWF) for occupant levels during normal periods are as follows:

Normal No. of occupants  =  30

Global unit flow rate  =            0.370 m3/day  (ref. 4(c) of Appendix III of the Guidelines)

Maximum ADWF =  30 x 0.370 m3/day  =  11.1 m3/day  =  0.128 l/s

As there will be no restaurant at the Site, it is foreseen that the quantity of the sewage generated from other cleaning and washing activities such as cleaning of staff quarters in a frequency of once a week will be insignificant.  Circulating water will be used for the water cascade or water features.  Therefore, no sewage will be generated by these features.

During festival days, there will be a significant increase in number of visitors in the Multi-Cultural Education Retreat cum Columbarium.  The estimated flow of sewage generated is shown in Table 7.1 and is stipulated as follows:

Maximum Sewage Generated = 60.8 m3/day  =  2.11 l/s (assumed 8 hours operation, 0900 - 1700)

Note that the above flow rate is based on a very conservative estimation which assumes that the visitors will utilise the sanitary facilities on a continuous basis during the open hours (from 9:00am to 5:00pm).  The maximum capacity of a W.C. should be limited to not more than 6L.

Table 7.1        Estimation of Sewage Generated in One Festival Day

Data

Total no. of female W.C. = 10

Total no. of male W.C. = 4

Total no. of male urinal = 7

 

Assumptions

1.       Volume of flushing water for 1 W.C. = 6 L (maximum) (1)

2.       Volume of flushing water for 1 urinal = 1 L (maximum)

3.       Volume of water used by 1 person for washing = 2 L (average)

4.       Average duration of 1 female occupied a W.C. = 2 min.

5.       Average duration of 1 male occupied a W.C. = 1 min.

6.       Average duration of 1 male occupied a urinal = 40 s

7.       Open hours of the site in a day (9:00am - 5:00pm)

Estimation of Total sewage Generated in One Festival Day

Number of female using 1 W.C. in one hour = 60 min./ 2 min. = 30

Number of male using 1 W.C. in one hour = 60 min./ 1 min. = 60

Number of male using 1 urinal in one hour = 60 min./ (40/60)min. = 90

 

Total volume of sewage generated by female in 1 hour = 30 x (6+2)L x 10 = 2,400 L

Total volume of sewage generated by male in 1 hour = {60 x (6+2)L x 4} + 90 x (1+2)L x 7} = 3,810 L

 

Total volume of sewage generated by visitors in 1 day = (2,400 + 3,810)L x 8 hrs = 49,680 L (49.7 m3)

 

Total number of visitors using toilet facilities in 1 day = (30 + 60 + 90) x 8 = 1,440

 

Total volume of sewage generated by occupants in 1 day = 11.1 m3 (see above)

 

Total volume of sewage generated in one festival day = 49.7 + 11.1 = 60.8 m3

Note:     (1) The 6 L flushing water for 1 W.C. is commonly used in HK and only the water closets that actually have a flushing water volume not more than 6L will be used

7.6                                      Sewage Disposal Scheme

Option 1: Discharge to the nearby existing sewage system (i.e. Tai Po STW via public sewer at Tai Po Industrial Estate)

Under this option, it is necessary to construct approximately 2 km of sewers of 225 mm in diameter running along Sha Lo Tung Road with the downstream end connected to an existing sewerage manhole at Ting Kok Road (See Figure 7.2).  Ultimately the sewage from the Site will be discharged to Tai Po STW.

The impact on the Tai Po STW should be insignificant after the commissioning of the Stage 5 upgrading works.  The maximum sewage generated from the Site is about 16+11.1=27.1 m3/day (ADWF), while the capacity of the Tai Po STW is about 120,000 m3/day (ADWF).  The increase in flow would be only about 0.023% of the capacity of the STW (ie 120,000 m3/day).  It should be noted that the maximum sewage volume generated from the Development Site will only happen on rare occasions.  Sewage volume during normal periods will be about 40% of the maximum flow.

The ground level at the southern part of the Development Site is about 203 mPD, while the ground level at the northern part of the Development Site is about 184 mPD.  A pumping station and rising mains are to be constructed to deliver the sewage from the southern part of the Development Site in the north.

The peak flow to be discharged into the downstream sewerage system will be controlled by the capacity of the pumping system and the size of the storage tank.  Using a larger storage tank can reduce the pumping rate as well as the sewage flow to be discharged into downstream sewers without overloading the existing sewers in the downstream area.  We consider that the maximum sewage generated from the Site is only about 27.1 m3/day (ADWF).  Assuming a storage tank of minimum size of 198 m3, the average flow of the collected peak sewage volume of 27.1 m3 to be discharged within a day to the downstream sewers is about 0.00012 m3/s.  The peak flow of the pumps installed is proposed to be 0.0005 m3/s.  The minimum size of the existing downstream sewer is 225 mm with a capacity of about 0.0155 m3/s.  The discharged sewage is only 3.2% of the capacity of the existing minimum downstream sewer.  Therefore, the impact to the downstream sewer is considered insignificant.  It is proposed to install a stand-by pump in case of mal-function of the working pump occurs.

As the peak sewage generated from the Site is not significant (only 27.1 m3/day (ADWF)) overloading of the sewage system downstream and the Tai Po Sewage Treatment Plant (STW) can be avoided through the use of a storage tank and pumping station.  Please note that the capacity of the Tai Po STW is about 120,000 m3/day (ADWF).  The increase in the flow to the Tai Po STW due to the Site is only 27.1 m3/day (ADWF) (assuming the peak flow condition).  The increase in flow would be only about 0.023% of the capacity of the Tai Po STW. The impact to the Tai Po STW is insignificant.  The recommended option is considered feasible and practical.

Option 2: On site sewage treatment plant and discharge to adjacent drainage system

On-site tertiary level sewage treatment facilities are recommended in Option 2 for treating sewage from the Site to a standard acceptable to Environmental Protection Department for discharge to the existing drainage system.

As the Development Site is bounded by Fung Yuen Valley SSSI to the south and Sha Lo Tung SSSI to the north, a 225 mm diameter stormwater rising main will be constructed at Sha Lo Tung Road to convey the treated effluent from the Development Site to the existing drainage system at Ting Kok Road.  The treated effluent would finally be discharged to Tolo Harbour.  The proposed sewage network is shown in Figure 7.3.

A sewage treatment plant will be constructed within the Development Site. The proposed location of the sewage treatment plant (STP) is shown in Figure 7.3.  The sewage treatment plant can be constructed underground and entirely within an enclosure (eg. beneath the landscaped area and within the Site) to minimize adverse environmental impacts.  The sewage treatment plant could be a commercially available prefabricated package plant with rotating biological contactor and chlorination disinfection installation.  The treatment rate is estimated to be about 120 m3/day.

The effluents should be treated to acceptable standards as stated in Table 7 in the “Technical Memorandum on Standards for Effluents Discharged into Drainage and Sewerage Systems, Inland and Coastal Waters” for discharge to the coastal waters of Tolo and Port Shelter Water Control Zones.  However, there is an environmental concern over the discharge of treated effluents into Tolo Harbour which is of low assimilative capacity in nature.  This option is hence not recommended.

Option 3: Deliver the sewage off Site by tanker

This option does not require the construction of a pumping station within the Site or any rising main along Sha Lo Tung Road, which are required for both Options 1 and 2.  The sewage generated from the Development Site will be stored in a storage tank within the Site. Up to a certain amount, the stored sewage will be delivered off site by tanker. The proposed location of the storage tank is shown in Figure 7.4.

The normal sewage flow generated from the Development Site is about 11.1 m3/day (ADWF) as estimated in Section 7.5.  It is equivalent to about 77.7 m3 per week.  Even for a maximum flow rate of 27.1 m3/day (ADWF), the effluent volume to be stored per week will be 189.7 m3.  There would be a need to construct a storage tank with a capacity of minimum 190 m3 to cater for the peak flow volume.  The stored sewage will be removed once a week.  During a normal week, it is estimated that 32 round trips of the tanker in one day would be required to empty the tank (assuming 6 m3 capacity).  If more sewage is to be delivered, the delivery schedule could be split into several days in order not to overload the existing public carriageway system.  However, this option has the potential risk of polluting the environment if leakage happens during the collection and transportation of the sewage.  It will also increase the traffic load on the Sha Lo Tung Road.  This option is therefore not recommended.

Table 7.2 Summarises the sewerage strategies for the proposed development.


Table 7.2      Sewage Disposal Options

Sewerage Disposal Strategy

Option 1

Discharge to the nearby existing sewerage system (i.e. Tai Po STW via public sewer at Tai Po Industrial Estate)

Option 2

On site sewage treatment plant and discharge to adjacent drainage system

Option 3

Deliver the sewage off Site by tanker

Implementation

 

(1) Construct an approximately 2000 m long 225mm diameter sewer from the Site running along Sha Lo Tung Road to the upstream end of the existing sewage network at Ting Kok Road. The sewage will finally be discharged to Tai Po STW.

(2) Construct Pumping Station and rising mains at the southern part of the Site to pump the flow to the south (ultimately to Tai Po STW).

(1) Fung Yuen Valley SSSI is located to the south of the Site and Sha Lo Tung SSSI is located to the north of the Site. No new effluent is allowed to be discharged into the vicinity of an SSSI.

(2) Provide on-site tertiary level sewage treatment plant capable of treating the sewage from the Site to a standard acceptable (by EPD) for discharge to the drainage system at Ting Kok Road, via the newly proposed drainage system at Sha Lo Tung Road.

(3) Tertiary treated effluent is finally discharged to Tolo Harbour.

(1) Construct a storage tank to store the sewage generated on the Site.

(2) Deliver the stored sewage off the Site by tanker at regular intervals.

 

Possible Constraint and Solution

(1) Require a piece of land to accommodate the pumping station and associated installation.

(2) Possible conflicts with existing utilities and other services under Ting Kok Road and Sha Lo Tung Road.

(3) Possible disturbance to the existing traffic across Ting Kok Road and Sha Lo Tun Road for sewer laying and utility diversion.

(4) Through careful route selection, appropriate temporary traffic management scheme and adoption of suitable construction technique, the impact could be minimised.

(5) Liaison with EPD and DSD regarding any spare capacity to accommodate the sewage generated from the Site and the programme for the completion of the Tai Po STW upgrading works.

(1) Requires a piece of land to accommodate the plant and associated installation.

(2) The treatment plant and the associated installation could be underground and entirely within an enclosure to minimise adverse impacts.

(3) Possible conflicts with existing utilities and other services under Sha Lo Tung Road during the pipe laying for the drainage system.

(4) By careful route selection, good design and implementation of temporary traffic management scheme and adoption of good construction method.  The impact could be minimized.

 

(1) Require a piece of land to accommodate the storage tank.  The land intake requirement is minimal.

(2) Increases the traffic load on Sha Lo Tung Road.

(3) To be overcome by regulating the sewage delivery schedule.

 

Recommendation

Recommended as the preferred option

Not recommended

Not recommended


7.7                                      Sewerage and Sewage Treatment during Special Festivals

A maximum number of 7,400 visitors per day are allowed to visit the Multi-Cultural Education Retreat and Columbarium during Ching Ming or Chung Yeung Festival (refer to Section 3.8).  It is foreseen that sewage generated would be abruptly increased during these festival days.  At least 10 female W.C., 4 male W.C. and 7 male urinals are assumed to be provided in the Multi-Cultural Education Retreat and Columbarium for public use during the operation phase.  According to Table 7.1, the estimated maximum sewage generated during festival days is 60.8 m3/day.  This flow rate is based on a very conservative estimation which assumes that the visitors will non-stop use the sanitary facilities during the open hours (from 9:00am to 5:00pm).  Nevertheless, the proposed storage tank of minimum size of 180 m3 is considerably sufficient (with a buffer of approximately 3 days withholding time to cater for the situation if the pumping facilities malfunctioned; usually the public holidays during Ching Ming and Chung Yeung Festival do not last more than three consecutive days) to cater for the abrupt increase in generated sewage during festival days.  As the sewage flow rate of 0.0005 m3/s will be controlled by the pump, the increase in flow to the Tai Po STW will be 43.2 m3/day, i.e. 0.036% of the capacity of the STW. 

It is concluded that the impact on the STW due to abrupt increase in sewage flow during festival days is insignificant.  In addition, the sewerage system shall be of leak-proof design and the sewerage storage tank should also be emptied regularly in particular before, during and immediately after the festivals.  A deodorizing facility, such as activated carbon, will be installed at the exhaust of the storage tank to control odour.  However, it should be noted that the storage tank is only required during emergency or when the pumping facilities malfunctioned.  The maintenance/repairing works will conducted over a period of less than 3 days.  Therefore, the onsite storage of sewage will be temporary and infrequent.  With the installation of a proper deodorizing facility and very infrequent temporary onsite storage of sewer, no potential odour problem will be envisaged.

The peak flow of the pump installed is proposed to be 0.0005 m3/s.  The minimum size of the existing downstream sewer is 225 mm with a capacity of about 0.0155 m3/s.  The discharged sewage is only 3.2% of the capacity of the existing minimum downstream sewer.  Therefore, the impact to the downstream sewer during festival days is considered insignificant.  Also, it is expected that blockage of sewer pipe is unlikely occurred in such a flow rate of the pump.

Approximately 3 portable toilets will be erected at the entrance of Sha Lo Tung Road (next to Ting Kok Road) as contingency measures.  In order to provide a contingency against leakage from the toilets, they will be surrounded by temporary intercept drains.  Cleaning up of these toilets will be conducted in mid-day such that the number of persons using a portable toilet could be maximized and the leakage from the toilets could be minimized.  Generally, the maximum number of persons using a portable toilet is 380 after every cleaning exercise.  Should the permanent sanitary facilities in the Development Site be closed due to malfunction or emergency maintenance, additional portable toilets can be arranged within a short period of time to cater the visitors, ie a total of 10 portable toilets can cater for a maximum of 380 x 10 x 2 = 7,600 visitors if cleaning exercise is performed. 

7.8                                      Proposed mitigation Measures

Assuming Option 1 is adopted, the following mitigation measures are proposed:

·            Installation of an approximately 2 km long 225 mm diameter twin sewerage rising mains from the Development Site running along Sha Lo Tung Road to the existing sewerage network at Ting Kok Road;

·            Installation of a stand-by pump (with a 100% standby pumping capacity) in case of mal-function of the working pump;

·           Construction of a storage tank (fitted with a level indicator and a high level alarm system, designed and constructed to comply with the Buildings (Standards of Sanitary Fitments, Plumbing, Drainage Works and Latrines) Regulations (Cap 123I) reg. 47A) of minimum 180m3 capacity, to give approximately three days withholding time over maximum visitor attendance over festival periods to cater for the situation if the pumping facilities malfunctioned;

·            As a statutory requirement, the storage tank and all sewers within the WGGs will be designed and constructed to comply with the Buildings (Standards of Sanitary Fitments, Plumbing, Drainage Works and Latrines) Regulations (Cap 123I) reg. 47A to ensure that they are watertight.  Through the circulation of drainage plans to the Building Authority, other requirements of WSD on the design and details of construction will be complied.  As such, the risk of leakage of sewage from the sewerage system is considered to be very low, through the use of the best quality piping materials (typical example: vitrified clay or PVC or concrete pipe, which are common materials for sewer and are anti-corrosive; materials selected will subject to result of detailed design of proposed sewerage) and provision of hatch box access covers within chambers, and 

·            A deodorizing facility (e.g. activated carbon) will be installed at the exhaust of the storage tank to control odour.  With the installation of a proper deodorizing facility and very infrequent temporary onsite storage of sewer, no potential odour nuisance to public is envisaged. 

An assessment of the impacts of sewage generation during festival days has also been considered.  With the following measures to manage the increase in sewage generation, no adverse impacts to the sewerage system are expected:

·            Provision of adequate permanent water closets and urinals in the complex;

·            Emptying of the sewage storage tank before and immediately after the festivals; and

·            Provision of portable toilets at the entrance of Sha Lo Tung road, next to Ting Kok Road for contingency purpose.

7.9                                      Conclusion and Recommendations

Taking into consideration the constraints of the Development Site, and the existing and planned sewage network in the region, three sewage disposal options for the development of the Site have been investigated.   In broad terms, the three proposed sewage disposal options are discharging to Tai Po Sewage Treatment Works, treatment on Site and removal off site.

Among the three options, the option of discharging the sewage to Tai Po Sewage Treatment Works is recommended.  The option of provision of on-site sewage treatment plant and removal of the sewage off site by tanker are not recommended.  The recommended option is considered feasible and practical given that the impacts to the downstream sewer and the Tai Po Sewage Treatment Works are considered insignificant.  The details of the recommended sewage disposal scheme will be further confirmed at the detailed design stage and close liaison will be carried out with relevant departments to approve the scheme.


 



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