3          PROJECT DESCRIPTION

 

3.1       General

 

The proposed development of the bathing beach at Lung Mei, Tai Po was established under this Assignment, through liaison with ArchSD, LCSD and CEDD. The current development layout and arrangement has been selected through critical review of key issues such as traffic, road safety, drainage impacts, sewerage impacts, beach building facilities, topography, marine, environmental impacts, reclamation, current and future development and design standards.

 

3.2       Land Formation for Car Park and Beach Building

 

The current land area opposite Lo Tsz Tin, south of Ting Kok Road, where the car park and beach building are to be located on are basically at the correct formation level and therefore, to completely form the land for the above facilities, there will be a need of around 21,000 m3 backfill material. The backfill will mostly come from outside sources but around 8,300 m3 will be available from within the site, which will mainly come from the insitu material in constructing the eastern box culvert and for the western drainage channel.

 

3.3       Traffic

 

The proposed Lung Mei beach facilities and carpark area will be accessible off Ting Kok Road. A single ingress/egress point will be provided. The proposed works involve local road widening, construction of drainage and sewerage pipelines and laying of utilities along the existing Ting Kok Road in the vicinity of the Project site.  Therefore excavation works will be required along the existing Ting Kok Road. However, to minimize interruption to traffic flow, temporary traffic management will be implemented during the construction stages as discussed in Section 2.2.2.

 

Based on an estimate of the quantities of sand, public fill and other construction materials and equipments required for the construction of this project, and taking into consideration that some of the construction materials would be transported to the site by barge, it has been estimated that the maximum construction traffic generated by this project would be about 50 trucks per day each way. 

 

3.4       Proposed Drainage Diversion Works for Lo Tsz River

 

The downstream of the existing Lo Tsz River is proposed to be diverted to the west of the Project site by about 70m.  The diversion scheme comprises a 3.7m wide drainage channel and a reinforced concrete box culvert, which will function as a transition for connecting the existing box culvert and the proposed drainage channel.  The drainage channel is proposed to be formed with sloping gabion embankments and rip-rap bedding. The proposed open channel is approximate 59m long with 5 layers gabion baskets. To enhance the environmental values and mitigate visual impact from Ting Kok Road, an L-shaped wall is proposed on top of the gabion baskets to provide additional spacing for vegetation. Moreover, a minimum 2 layers of Type IV rock amours are proposed at the channel outfall for scour protection.  The landscape issues along the proposed gabion channel will be discussed in Section 10. 

 

3.5       Proposed Drainage Diversion Works for Existing Box Culvert

 

The existing single cell box culvert at Lung Mei is proposed to be diverted with a right angle turn to the east by around 90m. The proposed diversion works include construction of a reinforced concrete box culvert, and also the re-profile of a section of the existing box culvert invert level with concrete.

 

To consider the visual impact from Tai Mei Tuk, the finishing of the proposed eastern box culvert will be consistent with its adjacent vertical seawall.  Moreover, additional planting area is proposed on the top of box culvert to enhance the environmental aspects of the works. 

 

For ease of construction and minimize the environmental impacts, the box culvert is proposed to be constructed as pre-cast and cast in-situ segments with toe protection along the proposed culvert.

 

3.6       Other Proposed Drainage Works

 

Seven existing gullies in the proximity of Lo Tsz Tin are proposed to be re-constructed for local widening of Ting Kok Road. 

 

A separate stormwater drainage system is proposed within the beach carpark. The proposed system comprises a petrol interceptor in compliance with EPD regulations, and a pipeline with diameters varying from 375mm to 750mm. The collected runoff within the carpark is proposed to be finally discharged to the sea through the proposed box culvert at Lo Tsz River.

 

3.7       Sewerage Works

 

It is proposed to collect all sewer and wastewater flow from the beach development. There will be 4 foul sewer manholes and one sewage holding tank proposed with a proposed sewer of 225mm diameter that will be aligned across the car park, across the existing Ting Kok Road and eventually connect to the existing trunk sewer by tapping into an existing foul sewer manhole.

 

3.8       Preliminary Design of Beach and Groyne Structures

 

The most appropriate orientation of the beach and groyne structures has been determined from mathematical modelling. The design beach profile has also been determined from modelling studies that examined the beach response to normal and storm wave conditions. From current assessment of grain size for the available beach sand sources and with reference to relevant design guidelines, the proposed designed slope of the beach will be constructed consisting of a 1:12.5 upper slope above +2.0mPD and 1:15 below, with the beach recharge offshore of the natural step consisting of a 1:25, as shown on Figures 2.8 and 2.9.

 

A wave modelling was carried out to assess the storm response upon a design construction profile and a design equilibrium profile. The sediment sizes used for the modelling were focused upon 0.4mm (although grain sizes of 0.2mm, 0.3mm and 0.5mm were also modelled) as this had been identified as the most probable sediment size to be used, which is an average representative of the random sieve analysis taken from samples taken from beaches in Hong Kong in late 2006, namely Lung Mei, Tai Po, Lower and Upper Cheung Sha Beach, Lantau Island, Golden Beach and Ping Chau Beach. However, Fill Management Division of CEDD has confirmed that sand sources from Hong Kong SAR should not be considered on environmental and political grounds. Therefore, sand sources from outside Hong Kong SAR should be investigated in the detailed design stage.

 

Sand source distributors for the proposed beach have been contracted and it was ascertained that sand sources of D50, from 0.2mm to 0.5mm, are currently available from HaikouHainan Province, NanSha, Guangdong Province, and Weihai, Shangdong province in Mainland China, as well as in Vietnam. However, the above distributors will not provide any particle size distribution results until they receive confirmation of any sand order, which should be further investigated in the Detailed Design stage. The sand source distributors understand the requirements specified in the WBTC 10/95 & WBTC 10/95A for the importation of sand from Mainland China by barges.

 

Notwithstanding the above, it is understood that the sand source for the Cheung Sha Replenishment in Lantau Island during the period from late 2006 to the first quarter of 2007 have been acquired from Zhujiang estuary (Shajiao) in Mainland China. Port Works Division of CEDD has also recently completed some sand replenishment works at Peng Chau where the sand was sourced from Ma Wan and Zhujiang estuary (Shajiao), Mainland China. 

 

The sand quality will be based on similar requirements in respect to sand for a recreational beach as set out in Section 3.6 of the Port Works Design Manual: Part 5 – Guide to Design of Beaches and shall comply with the requirements as promulgated in WBTC No. 10/1995.

 

It has been ascertained that the required sand fill required for beach is 37,500m3 of sand.

 

The extreme wave conditions established by the modelling studies were used to determine an appropriate armour rock size, beach crest height, and groyne cross-section. Therefore, there will be two rock groynes, one 100m on the east and the other 120m on the western end of the beach. The groynes will be protecting the bathing beach using natural rock armour construction. It is anticipated the recharging of the beach with sand and the groyne construction under low water mark will be carried by marine based plant and equipments.

 

During the construction works, there will be a silt curtain to minimise the water quality impact due to the sand filling and dredging works.

  

Finally, at the operation stage, there will be a shark prevention net at the perimeter of the bathing beach, surrounding the toe and side of the beach.

 

3.9       Beach Layout

 

The proposed orientation of the beach is aligned at 145o to the north and the wave and sediment modelling results presented in Appendix B shows that the net longshore drift of the sediment is not significant (10 to 150m3 per year) for sediment sizes of 0.25mm, 0.3mm and 0.5mm. However, with the groynes in position, the sediment will eventually drift towards the western groyne and in general be contained by the groynes as shown on Figures 2.7 to 2.9. In addition, there is no significant problem with cross-shore sediment movement under storm wave conditions. Therefore, no sand loss is anticipated for the proposed bathing beach and as such, no environmental impact would be induced on the adjacent environmental sensitive areas.

 

Therefore, under the operational phase of the beach development, the two groynes at either end of the beach will contain the small net drift amount that has been identified in the wave and sediment modelling results presented under Appendix B. Consequently, the assessment demonstrated that there will be no ecological impacts to the environment, in particularly the SSSI on the west of the Project site and those corals identified in the EIA study.

 

3.10     Beach Building Facilities

 

The bathing facilities for this development have designed by ArchSD and will mainly consist of 3 building structures as discussed below and shown on Figure 2.4:

 

·       There will be a one level building near the Ting Kok Road and it will comprise of the male changing rooms, toilets and shower rooms, this will also include all the associated E&M facilities. It will have a terrace roof planted with trees. This building will also accommodate the refuse collection point ;

 

·       The other two structures will be adjacent to the beach, facing the sea. The building on the eastern side will have one level, which will comprise of the family and female changing rooms, toilets and shower rooms; this will also include all the associated E&M facilities. Outdoor shower facilities will be situated at the side of this building; and

 

·       The third building on the west will basically be a two storey structure, which will comprise of the ancillary facilities including management office, lookout/surveillance post, first aid room, solar water tank & pump room, fire services tank room, water tank room, fast food kiosk, etc. It will also have equipment / machinery stores for catamarans, motorized boats, beach transporters, beach cleansing and sand levelling machines, etc., as well as goods stores.  A sun shading will be situated at the west of the building to accommodate a seating area.

 

A Category 5 (Substances Giving Off Inflammable Vapour) dangerous good (DG) store is required for storing Oil dispersant, Motor spirit, petrol, Kerosene and Lubricant for operation of machinery. In addition, lacquers, varnish and paint thinner will also be stored for painting maintenance. The DG store will be located within the administrative building at the carpark level, which can be reached directly by DG vehicle for delivery of DG and by fire appliances during emergency. The storage of containerized LPG and containerized chlorine are not expected, but small quantity of bleaching solution (Sodium hypochlorite, Cat. 4 D.G.), less than 250 litres which are below the FSD exempted quantities, will be stored at beach for cleansing purpose e.g. toilet/changing room.

 

The Water/FS Pumps and the Mechanical Ventilation of plant rooms would be in operation for 24 hours. There are 3 numbers of pumps in the water tank room and 3 numbers of pumps in the FS pump room. Both of the pump rooms would be on Level 2 (see Appendix I for building elevation) and mechanical ventilation fans would be provided at each plant room.

 

There will also be a fee paying car park, which will accommodate 100 private cars, 10 motorcycles and 3 coaches, with drop off arrangements. In addition, there will be two lookout towers at the beach level.

 

Landscaping works are planned around the perimeter of the car park as well as the roof terraces above the changing rooms, along the groynes and also above the proposed culvert at the east section of the bathing beach.

 

3.11     Preliminary Proposed Marine Facilities

 

There are 38 mooring buoys for the leisure yachts, which are located in the vicinity of the proposed footprint of the beach development. For the beach operation, it was suggested to Marine Department (MD) that 12 of the existing mooring buoys should be permanently relocated as shown on Figure 3.1. The relocations are proposed in the vicinity of the Lung Mei waters taking into account the following criteria:

 

·          Provision of about 50m clearance from the Shark Prevention Net, which should be sufficient clearance from the leisure yachts in light of the information provided by MD on the chain lengths attached to the buoy and will also be sufficient clearance for future maintenance of the Shark Prevention Net;

·          Sufficient clearance between the leisure yachts, which are also determined according to the chain lengths of the affected buoys;

·          Away from the Ting Kok SSSI as far as possible;

·          Sufficient water depth for yachts access (the proposed relocation will be further confirmed with the latest sounding survey records);

·          Avoid disturbances to the waterway for access to the existing landing steps at Tak Mei Tuk;

·          Minimizing interfaces with the existing water sports activity area of Tai Mei Tuk Water Sports Centre (Approximate extent of the area is shown on Figure 3.1).

 

Moreover, the marine facilities arrangement proposal as shown on Figure 3.1 will be subject to the agreement with the relevant government departments as well as to the latest sounding survey prior to commencement of the construction works.

 

3.12     Operation Phase

 

The operation phase of the Proposed Beach Development is considered as commencement of the handover date to LSCD so that the proposed measures recommended under EM&A should be carried out as appropriate after the handover. However, there may be a time lapse between the handover date and the formal opening for public use due to the application of the beach gazette by LCSD.

 

Furthermore, the proposed swimming area, which will be about 200m long and 200m wide, will be protected with shark prevention net located at the perimeter of the swimming area.  The proposed swimming area together with a buffer zone will fall within the gazette beach boundary.

 

The normal beach operating hours as well as the PA system operation hours are as follows –

 

Period

Time

Remark

April, May, September, October

9:00 a.m. - 6:00 p.m.

Daily

June, July, August

9:00 a.m. - 6:00 p.m.

Weekdays

8:00 a.m. - 7:00 p.m.

Saturdays, Sundays &    Public Holidays

November, December,       January, February, March

8:00 a.m. - 5:00 p.m.

Daily

 

3.13     Maintenance of Sandy Beach

 

As discussed in Section 3.9, the arrangement of the beach groynes will prevent any sand loss and therefore, regular sand replenishment is not anticipated. However if sand replenishment on the proposed beach is required in the future due to possible sand loss occurring after extreme storm conditions, such as the passing of extreme typhoons, it is anticipated that in such case, sand replenishment will be carried out using land plant and the sand will be placed above the mean high water level. Eventually, the beach will reprofile due to naturally occurring environmental factors such as wave actions, current movements and wind.

3.14     Construction Programme

 

The Proposed Bathing Beach Development will be carried out under two construction contracts. The beach buildings and associated facilities will be constructed under one construction contract, whilst the other civil engineering works will under a separate contract.

 

The construction works are currently programmed to commence in December 2008 and the works are scheduled to be completed within two years, exclusive of delays due to issues such as inclement weather. The programme is shown on Figure 3.2.

 

3.15     Project Interface

 

The Tolo Harbour Sewerage of Unsewered Areas Stage I Phase IIC (Agreement No. CE 18/94) will carry out works connecting the unsewered areas from Ting Kok village to Lung Mei village, which are in the vicinity of the bathing beach development. The current programme for the sewerage construction works is November 2008 to November 2010, which coincidently will be concurrent with the anticipated construction period for this Proposed Bathing Beach Development project. Therefore, it is anticipated that the construction works for Assignment No. CE 18/94 might have influence on the EIA of this proposed bathing beach, in particular the construction phase. As such, cumulative impacts from the above project, if any, will be assessed in this EIA Report.  With the implementation of the sewerage connection (expect to be up to a 60% connection rate) and the gazette of the Tolo Harbour Sewerage of Unsewered Areas Stage I Phase IIC (Agreement No. CE 18/94) including Lung Mei area, as part of the Sewerage Master Plan Works for Tolo Harbour Catchment, the water quality at Lung Mei will be improved and guaranteed, thereby facilitating the operation of this bathing beach.