2                                  Consideration of Alternatives

2.1                            Introduction

In accordance with the requirements of Sections 3.3.3 to 3.3.5 of the EIA Study Brief, this Section describes the site selection process for the identification of the site for the development of the wind turbine.  Consideration of alternatives also includes plant and equipment delivery modes and routes.  

2.2                            Consideration of Alternative Sites

2.2.1                      Introduction

A rigorous site selection process has been conducted to identify suitable areas for the development of the wind turbine.   A potential area must have the following essential characteristics to be considered in the selection process:

·           sufficient wind resource for operation of a commercial scale wind turbine;

·           the area must be on land ([1]); and

·           the area must have access to CLP Power’s transmission network. 

2.2.22.2.1      Identification of Potential Areas

Considerations given in the site selection process can be broadly divided into three main categories, namely grid interface; environmental, physical and social constraints and wind resource.

Wind Resource

A preliminary assessment of the wind resource within the Hong Kong SAR was undertaken using the industry standard model for wind flow modelling (Wind Atlas Analysis and Application Programme (WAsP)).   The WAsP model is recognised as the industry standard for wind flow modelling and was developed by the Wind Energy and Atmospheric Physics Department at the Risø National Laboratory in Denmark.  The preliminary results were sufficient to identify sites of potential interest.  

Figure 2.2a presents a map of relative wind resources within the CLP Power supply area.

Grid Interface

The main consideration in terms of grid interface in the site selection process is the ability to connect the wind turbine with CLP Power’s existing supply grid through a land cable. 

Environmental, Physical and Social Constraints

Areas within Hong Kong SAR that are considered as constraints for locating a wind turbine were mapped.  These areas were excluded from further consideration. 

The constraints were classified into those that were considered to be environmental, physical and social, respectively, in nature.  Areas that are generally not considered to have environmental, physical or social constraints to the proposed wind turbine are considered to be unconstrained areas. 

The constraints identified under each of these subheadings are summarised in Table 2.2a and presented in Figures 2.2b to 2.2m.

Table 2.2a      Summary and Classification of Constraints

Exclusion Constraints

Environmental

·Country Parks

·Special Areas

·Ramsar Sites

·Wild Animal Protection Areas

·Sites of Special Scientific Interest (SSSI)

·Sea Turtle Nesting Ground

 

Physical

·Gazetted Bathing Beaches

·Seawater Intake Points

·Areas with Residential and Commercial Premises

·Development height restrictions in the vicinity of the Hong Kong Disneyland Resort

·Building height restrictions associated with the safe operation of the Hong Kong Airport

·People’s Liberation Army Firing Range

 

Social

·Areas with population density greater than 30,000 per km2

Figure 2.2n presents a composite constraints map.

Identification of Potential Areas

The composite constraints map (see Figure 2.2n) was overlaid with the wind resource map (see Figure 2.2a) to establish the unconstrained areas with reasonable wind resource potential.

The siting of the wind turbine must comply with the Airport Height Restriction (AHR) which was established under the Hong Kong Airport (Control of Obstructions) Ordinance (Cap 301).  Under the ordinance, there are prescribed areas within which no building or structure should exceed a specified height above the principal datum.  These prescribed areas and their associated building height restrictions are shown on the AHR series of plans published by the Government.  These restrictions are absolute and, according to the Civil Aviation Department (CAD), exemptions could only be granted by the Secretary for Housing, Planning and Lands if a structure exceeding the AHR is required for an overriding public interest.

In screening potential areas with regard to the AHR, it has been assumed that the total height of the wind turbine (including the blade) is approximately 80m.  The resulting height of the wind turbine structure is expressed in metres above the principal datum (mPD), is then compared with the published building height restrictions for the area concerned to check for compliance.   The potential areas which comply with the AHR were considered further.

A total of 73 potential areas being 14 areas with the 1st and 2nd highest wind energy resource (see Figure 2.2o) and 59 areas with the 3rd highest wind energy resource (see Figure 2.2p) were identified.   The aim was to select a short list of 2 or 3 sites for site-specific wind monitoring. 

2.2.32.2.2      Elimination of Potential Areas

Box 2.2a lists the 13 environmental, planning and engineering criteria used for the comparative assessment of the long list of potential areas.

1.              Permitting risk and complexity

2.              Strategic and District planning ([2])

3.              Conservation importance

4.              Noise

5.              Hazards ([3])

6.              Land availability and potential to develop into a wind farm

7.              Site slope

8.              Site access (for construction and maintenance)

9.              Reclamation (for formation of the wind turbine site or temporary barging point for delivery of construction materials)

10.          Accessibility to visitors

11.          Proximity to CLP Power 11kV grid and connection complexity

12.          Proximity to CLP Power 132kV and 400kV overhead cables

13.          Proximity to helicopter flight path or paragliding areas

Box 2.2a         Criteria Used for Assessment of the Long List of Potential Areas ([4])

Each potential area was assessed by the team of wind energy specialists, environmental specialists and engineers, and assigned a score/rank of 1 to 3 against each criterion.  A rank of 1 would mean that the area could be considered to perform poorly, whereas, a 3 would be a reflection that the location performs well against that criterion.   All criteria except for wind energy had the same weighting.   The composite score/rank of all the criteria listed in Box 2.2a was then combined with the score/rank for wind resource potential.  Following the approach, the ranking for wind energy potential would contribute 50% to the overall composite score/rank.  This was considered appropriate as the availability of sufficient wind energy at a particular location was an important factor in determining whether it would be possible to operate a commercial scale wind turbine at the location.

Screening of the 14 Potential Areas with the Top Two Levels of Wind Resource

The less favourable potential areas for siting of a wind turbine were eliminated.   Eight (including Robin’s Nest, Pok To Yan, Tai A Chau, Siu A Chau, Jin Island, East of Hung Uk, Kau Sai Chau and Shek Kwu Chau) out of the 14 long-listed potential areas were retained and formed the interim short-list of potential areas.   The site characteristics of these areas are described in Table 2.2b.

Site visits were conducted to confirm the findings of the screening exercise.   Two were found to have severe access problems (Po To Yan and Jin Island), two are remote areas (Siu A Chau and Tai A Chau) and two would potentially interfere with the operation of existing radio equipment (East of Hung Uk and Shek Kwu Chau).   Robins’ Nest and Kau Sai Chau were retained for further consideration.

As it is targeted to select a short-list of 3 potential areas for undertaking site specific wind resource monitoring, the potential areas with the 3rd highest level of wind resource were assessed to identify one more site for further consideration. 

 


Table 2.2b      Site Description

No.

Name

Description

1

Robin's Nest

Robin’s Nest is located in a high (elevation > 450 mPD) mountain range in the north-eastern New Territories (see Figure 2.2q).  The potential area identified is about 10 ha and is approximately 500 m from the nearest access road, which is a single-lane paved vehicular track.  The gradient of most of the area is greater than 30%.  Ecological habitats within the area comprise mainly of grassland.  There is a television broadcasting station at lower altitude to the west of the potential area.  Robin’s Nest is adjacent to the Border Closed Area and the nearest residential areas are the villages at least 1 km away at the foothills of the mountain range.

6

Kau Sai Chau

Kau Sai Chau is located at approximately 3.5km from Sai Kung town centre and is one of the islands in Port Shelter (see Figure 2.2r).  The northern part of the island is currently used as a golf course.  A fish culture zone is located to the south of the island.  Four potential areas have been identified on the southern part of the island giving a total available area of about 21ha.   These potential areas are all located on the top of a hill and 50% of the areas have a gradient between 10 and 20%.  Some village houses and a Hung Shing Temple are located at about 200m from the nearest potential area.  The other three potential areas are located more than 600m away from these village houses.  These potential areas can be reached by existing footpathswhich are linked to the Kau Sai Chau Golf Course and piers at the southern tip of the island.  The main pier serves the golf course and other smaller piers at the southern tip of the island near the Hung Shing Temple serve Kau Sai Village.  Ferry services are operated between these piers and Sai Kung town centre. 

 

7

Jin Island

The island is located immediately south of Kau Sai Chau (see Figure 2.2s).  It is relatively remote and undisturbed.  There is no pier/jetty or road on this island.  Two potential areas have been identified on this island, both at the hill tops, giving a total available area of about 32ha.  More than 0.5ha of the potential areas have a gradient less than 10%.  The habitat is mainly mixed shrubland and woodland.  Some village houses are located at approximately 380m away from the boundary of the one of the potential areas.   The other potential area is located more than 600m away from the nearest village houses.

 

9

East of Hung Uk

The potential area identified is on a hill to the east of Hung Uk on the Clear Water Bay Peninsula (see Figure 2.2t).  The available area is about 3.4ha and the whole site is within a Conservation Area.  The habitat within the site is woodland with patches of cultivation.  To the south of the potential area is Sheung Yeung Shan, which is zoned as a Country Park area.  More than 0.5ha of the potential area has a gradient less than 10%.  The potential area can be reached by an existing footpath, which is the north entrance to the High Junk Peak Country Trail.  The nearest access road is Clear Water Bay Road, which is only 90m away.  The area is surrounded by low-density residential developments.  The nearest development is Hung Uk, which is at about 90m to the west of the area.

 

11

Shek Kwu Chau

The island is situated to the west of the relatively densely populated Cheung Chau (see Figure 2.2u).  The island is relatively remote and undisturbed.  The only development on the island is the drug rehabilitation centre.  There is an access road from the pier to the rehabilitation centre.  The potential area identified is located in the southern part of the island, at about 75m away from the nearest access road.  The centre part of the potential area is not suitable for the development of the wind turbine due to aviation height restrictions.  The area of the potential area (excluding the centre part) is about 3ha.  The gradient of the potential area is greater than 30%.  The main habitat on the island is shrubland and grassland.  The drug rehabilitation centre is located within 300m of the potential area.

12

Pok To Yan

Pok To Yan is a hilly area, located approximately 2km to the south of Tung Chung New Town on Lantau (see Figure 2.2v).  The potential area identified is about 1 ha and is approximately 700m from the nearest access road.  The gradient of most of the area is greater than 30%.  The habitat of the area is mainly mixed shrubland and grassland with a patch of woodland.  The site is adjacent to Pok To Yan and Por Kai Shan Site of Special Scientific Interest (SSSI) and the North Lantau Country Park.  The site is located within the proposed North Lantau Country Park Extension area.  The nearest Noise Sensitive Receivers are village houses located at approximately 640 m away with very limited topographical screening.  The nearest high-rise residential building in Tung Chung New Town is located at about 840 m from the site boundary.

 

13

Siu A Chau

Siu A Chau, which is one of the Soko Islands group, lies in the south-western waters of Hong Kong and is relatively undisturbed and remote (see Figure 2.2w).  The island is situated approximately 2km to the south of Lantau and about 10km to the south-west of Cheung Chau.  Situated to the south of the Adamasta Channel, the site lies near the southern boundary of the Hong Kong SAR

There is no major development on the island.  A low-level radioactive waste store is located to the southeast of the potential area.  There is a small jetty near the previous Siu A Chau Tsuen and a dedicated jetty serving the low level radioactive waste store.  The potential area is about 4 ha and is located in the north-western part of the island.  More than 0.5ha of the potential area has a gradient between 10 and 20%.  The main habitat of the potential area is mixed shrubland and grassland with some woodland.

 

14

Tai A Chau

The island, which is one of the Soko Islands group, is situated to the south-west of Hong Kong and is remote (see Figure 2.2x).  The island was previously used as a refugee detention centre but it is now vacant and the buildings have been removed.  There is a pier on the island and access roads to the central parts of the island.  The potential area identified for the development of the wind turbine is about 11.2ha, located at the south-western part of the island.  Although 60% of the site has gradient greater than 30%, over 0.5ha of the area is on land with gradient between 10 and 20%.  The habitat of the potential area is mainly grassland and mixed shrubland with patches of wetland and woodland.

 

 

 

 


for renewable energy.  Issues relating to the operation of Helipad CC03 have been resolved in consultation with the Government Flying Services (GFS) and Civil Aviation Department (CAD).  It is therefore recommended that Hei Ling Chau be included in the short list of potential areas for further evaluation.

Summary of the Screening of the 59 Potential Areas with the Third Highest Wind Resource

The screening process was repeated for the 59 potential areas with the 3rd highest wind resource in order to identify another site for further consideration.   Using the same screening procedures, 7 interim short-listed areas (including South of Tung Chung, Lo Fu Tau, Ha Shan Tuk, East of Sha Lo Wan, Black Point, Hei Ling Chau and Shan Mei) were identified. 

The potential area at Black Point (see Figure 2.2y) encroaches on the proposed WENT Landfill Extension which is an important component of future waste management strategy for Hong Kong.  The development of a wind turbine at this location will constrain the development of the landfill extension and therefore it is not recommended to consider this area further.   As the potential area at East of Sha Lo Wan encroaches on the alignment of the Ngong Ping 360 Cable Car, this potential area will not be considered further (see Figure 2.2z).

Site visits were undertaken to the other 5 potential areas.   The entire areas of the South of Tung Chung and Lo Fu Tau sites are within a gazetted proposed Country Park (see Figures 2.2aa and 2.2ab).   Participants at the stakeholders’ consultation meeting held in December 2004 expressed concerns about setting a precedent for allowing development within an established Country Park or gazetted proposed Country Park.   It is therefore not recommended to take these two areas forward for further evaluation. 

The Ha Shan Tuk site lies within a “CA” zone (see Figure 2.2ac), and therefore is subject to the rezoning application process under the Town Planning Ordinance and the statutory Environmental Impact Assessment (EIA) process even for the installation of a wind monitoring station.  The requirements for the above statutory processes introduce additional uncertainties into the project programme.  It is therefore not recommended for further evaluation.

The Shan Mei site (see Figure 2.2ad) is small and is relatively close to overhead power transmission lines and inhabited buildings in Kwai Tei New Village and Fo Tan Cottage Area.   The small size of the area, its proximity to residential properties and the lack of access make Shan Mei unfavourable for a wind turbine.   It is therefore not recommended for further evaluation.

Access to Hei Ling Chau site (see Figure 2.2ae) is not a concern since regular educational visits to the island are currently organised and supported by Correctional Services Department (CSD) using an established system managed by CSD.  CSD is also implementing an Environmental Management System at these correctional institutions and the department has expressed its initial support Site Screening Process

Table 2.2c summarises the site screening exercise and outlines how the short-listed sites are identified.

Table 2.2c      Summary of the Site Screening Exercise

Step

Potential Areas Reviewed

Screening Method

Result

1

Entire CLP Power supply area (on land only)

Constraints mapping and wind energy resource mapping. Checking of compliance with aviation height restriction

73 potential areas (14 areas with the 1st and 2nd highest wind energy resource and 59 areas with the 3rd highest wind energy resource)

 

2 Stakeholder (NGOs) consultation workshops to discuss the site screening exercise and findings.  Relevant Government Departments have also been engaged.

 

2

A long list of 14 potential areas with the 1st and 2nd highest wind energy resource

Comparative assessment using ranking criteria and eliminates areas with low score

 

An interim short-list of 8 potential areas for further consideration

3

An interim short-list of 8 potential areas

Observations from site visits

A short-listed of 2 potential areas for further consideration

 

4

A long list of 59 potential areas with the 3rd highest wind energy resource aiming to identify another potential area to achieve a total of 3 potential areas

 

Comparative assessment using ranking criteria and eliminates areas with low score

 

An interim short list of 7 potential areas for further consideration

5

An interim short list of 7 potential areas

Observations from site visits

Identified 4 potential areas at Hei Ling Chau, Shan Mei, South of Tung Chung and Lo Fu Tau for further consideration

 

6

6 potential areas (including 2 identified from Step 3 and 4 identified from Step 5)

Stakeholders consultation and further assessment taking account of stakeholders’ feedbacks

A short list of 3 potential areas including Robin’s Nest, Kau Sai Chau and Hei Ling Chau was recommended for further consideration.  Relevant Government Departments have been engaged and updated the findings of the site selection processes.

Note:

(a)       Twenty-five stakeholder consultation or liaison meetings (including NGOs, ACE, CAD, GFS, CSD, PlanD, EPD, EMSD, LandsD) were held.  A list of the stakeholder meetings held is presented in Annex E.

Further Review of the Robin’s Nest Site

The existing vehicular access from Wo Keng Shan Road to the peak of the Robin’s Nest is via a very steep (some sections with a gradient greater than 20%), long (about 3km) and narrow single-track access road.   Concerns were raised regarding vehicular access to the Robin’s Nest site.   A more detailed review of the engineering constraints associated with the delivery of the wind turbine to the site was undertaken and concluded that the risk posed to the safety of the construction workforce and the integrity of the equipment was excessive.   The ascent of the delivery vehicles would be difficult and dangerous, particularly at certain bends where there is limited space for a vehicle to turn, even if the roads were upgraded.   This site was therefore eliminated from further consideration.

Alternative Sites for Development of the Wind Turbine

The site selection process has identified that Kau Sai Chau and Hei Ling Chau be selected for further consideration.   In a comparative assessment of the two sites, the relative merits of the sites were evaluated with respect to wind resource, engineering, environmental ([5]), planning and economic considerations.  For the wind resource consideration, wind monitoring stations were constructed at these sites to collect site specific data.   The wind monitoring programme indicates that the wind resources at Kau Sai Chau and Hei Ling Chau are substantially the same.

Due to the topography of the Kau Site Chau site, the construction of the access road for the Kau Sai Chau site is expected to be much more complex (in terms of length of the access road, vegetation clearance, extent of slope works, steep gradient, etc) than that for Hei Ling Chau site.   The water depth at the Kau Sai Chau pier is shallow and will only be accessible to construction barges during high tide.   It may therefore require delivery of the plant and equipment at restricted hours.   From an engineering perspective, it is considered that Hei Ling Chau site is preferred to the Kau Sai Chau site.

An initial assessment of the potential environmental impacts associated with the construction and operation of the wind turbine at each of the sites revealed that there are no insurmountable environmental impacts for both sites.    However, the construction of the access road at the Kau Sai Chau site will require clearance of a larger area of vegetation and will entail a relatively larger environmental impact overall.   Therefore, the Hei Ling Chau site is preferred to Kau Sai Chau site in terms of environmental consideration.

Due to the close proximity of the existing pier at Kau Sai Chau (which will be used to deliver the construction plant and equipment) to the fish culture zone, there may be concerns from the fishermen.   This will increase the degree of uncertainty in the development programme and may delay the Project.   The Kau Sai Chau site also requires a longer construction period and higher capital cost.   Taking into consideration the overall merits of the two sites with respect to wind resource, engineering, environmental, planning and economic considerations, the Hei Ling Chau site demonstrated advantages over the Kau Sai Chau site.  Therefore, although both the Hei Ling Chau site and Kau Sai Chau site are both feasible sites for the wind turbine pilot demonstration, the Hei Ling Chau site is selected as the preferred site.

2.3                            Consideration of Alternative Locations for the Project Site

Figure 2.2ae shows the potential area on Hei Ling Chau for development of the wind turbine.   The area is at the southern end of the island and is away from any inhabited facilities.

At the northern end of the potential area is a helicopter landing pad that is used by the Government Flying Services (GFS), mostly as a landing point in the event of an emergency on the island.   The approach and exit paths to the helipad are shown as the area between the two red lines.   The wind turbine must not intrude into this zone.  Pursuant to consultations with GFS, a separation distance of at least 150m between the centre of the wind turbine tower and the helipad should be provided. 

Hei Ling Chau falls within the Hong Kong Airport Height Restriction Zone.  At the northern end of the potential area, the level of the zone is at 169 mPD, while at the southern end the level is 164 mPD.   CAD has advised that they have no adverse comment on the proposed location, provided the wind turbine overall height is in compliance with the airport height restriction and suitable lighting and markings on the turbine are adopted.

2.3.1                      Potential Locations for the Project Site

The majority of the potential area is vegetated and hilly with little or no established means of access.   The tallest peak is on the western side of the area, while to the east the land falls away to the sea.  At the north end there is a contractor’s storage area, which has been subject to re-grading and is relatively flat. 

The ‘peak’ area is not preferred due to:

·            potential wind shear effects;

·            the need for large amounts of earthworks that would be necessary to form an access to the site and a working platform for construction; and

·            the higher ground level (about 120 mPD) and lower airport height restriction zone (about 164 mPD) which would limit the height available for the turbine to around 44m, which is not acceptable.

The ‘valley’ area is not preferred due to:

·            the need for large amounts of earthworks that would be necessary to form an access to the site and a working platform for construction; and

·            the shielding effects of the higher ground to the north, when the wind is from that direction.

The ‘ridge’ area is not preferred due to:

·            the need for earthworks that would be necessary to form a working platform for construction; and

·            the higher ground level and lower airport height restriction zone which would limit the height available for the turbine.

The preferred location is the Contractor’s Storage Area as:

·            it is directly accessible from existing, paved access roads;

·            it is relative flat and minimal earthworks would be required to form a working platform;

·            its level at about 70mPD together with the airport height restriction at about 169 mPD allows a turbine height of approximately 100m;

·            it is not shielded from prevailing winds and would be unlikely to be subject to wind shear or other turbulence; and

·            it is noted that the wind monitoring mast was located in the contractor’s storage area and therefore no extrapolation of wind data will be necessary if the turbine is also located there.

2.3.2                      Alternative Site Layout and Size

Although the turbine, when erected, will occupy relatively little land, the area needed during construction and erection will be larger in order to accommodate cranes and provide space to place the turbine components prior to their being lifted into place.  The basic size requirement (about 90m x 50m (4,500m2) and generic site layout are shown in Figure 2.3a.   It need not necessarily be of this shape and could be reconfigured to suit a site’s particular constraints, but the overall area required would remain essentially the same.

It is also important that to allow the turbine components to be safely off-loaded and stored and to enable safe and secure handling and lifting of the components, the site area should be relatively flat.

During the development of the erection scheme, the site layout requirements were developed based on the likely size of wind turbine to be adopted.   This indicates that a slightly large area is required for the crane assembly.   The minimum length of crane jib to be fabricated on the ground is around 90m long.  This length together with the storage space and site width of about 50m determined the size of temporary works site area that is required.

Figure 2.3a     Basic Size Requirement and Generic Layout of Wind Turbine

The actual area indicated in Figure 3.1b is 100m x 54m to allow for a slight variation in typical plant employed locally from Hong Kong for the erection.

As can be seen from Figures 2.4d and Figure 3.1b, any existing flat land adjacent to the access roads has already been occupied by CSD facilities.  The existing CSD’s contractor storage area satisfies the basic size requirement and is relatively flat which minimises the site formation works and direct impact on the adjacent habitats.   The proposed layout ensures that the wind turbine is at least 150m away from the 220o or 100o flight sector of the helipad (see Figure 2.2ae).   If the orientation of the site is rotated about 90o anti-clockwise (ie Option 1 in Figure 2.3b), the site layout could still fit within the contractor storage area without significant vegetation clearance.  However, the wind turbine will be too close (ie <150m) to the approach and exit sectors of the helipad.  It will not be acceptable to GFS and CAD.  If the proposed site layout is rotated about 45o (ie Option 2 in Figure 2.3b), the wind turbine tower will be 150m away from the 220o line of the GFS helicopter approach sector.  However, it will require significant earthworks and clearance of vegetations which are not preferred.

The environmental benefits associated with this proposed site layout include:

·           minimising the potential impacts on existing flora and fauna as the area is currently used as a contractor storage area; and

·           minimising site formation works and hence potential surplus of excavated material requiring off -site disposal;

Figure 3.1b is considered as the preferred layout and adopted in this EIA Study. 

2.4                            Consideration of Alternative Delivery Modes and Routes

2.4.1                      Marine Access

There are two existing jetties on the Hei Ling Chau Island.  One is located at the northern part of the island near the Hei Ling Chau Refuse Transfer Station.  The other is at the southern side of the island near the Hei Ling Chau Addiction Treatment Centre (Annex).   A hydrographical survey has been carried out at the existing berthing facilities (see Figures 2.4a to 2.4c) confirmed that there are sufficient water depth at both jetties and hence no dredging of the approach channel and/or the berthing area will be required.

2.4.2                      Air Lifting

Airlifting of the key wind turbine components (blades (up to 5 tonnes each), tower sections (up to 42 tonnes each) and nacelle (up to 43 tonnes)) to the Project Site has also been considered.  If this is possible, it will avoid or reduce the enabling works for the existing roads or avoid building a new access road.   The largest, commercially available, heavy lift helicopter in this region has a maximum lift capacity of about 20 tonnes.   Therefore this method is not feasible for the lifting of the tower section and nacelle. 

The commercially available helicopters in Hong Kong have a maximum lift capacity of about 1 tonne and therefore will not be able to lift the blades to the Project Site.   There will be considerable logistical problems in getting a suitable size helicopter to Hong Kong at the time of the blade erection and some considerable advance planning will be required.   Even if the blades can be airlifted to the Project Site, it cannot avoid the need for enabling works for the existing roads or building a new access road for the transportation of the tower sections and nacelle.  It is therefore considered that airlifting of the nacelle and tower sections is not feasible. 

2.4.3                      Road Access

Existing Road Network on Hei Ling Chau

The road infrastructure is well-established and the potential area can be easily reached by road.   However, the size and weight of the of the wind turbine components (nacelle, blades and steel tower sections) to be transported and the necessary crane for erection of the wind turbine will have a significant impact on the existing or proposed transport routes.

An initial transportation study has been carried out to determine the feasibility and impact of the transportation of the larger components to the island sites by marine and overland transport.   Further study, in conjunction with a transportation contractor, has also been undertaken to allow the impacts of such transport to be minimised.

Items to be Transported

Turbine Components:  The turbine components adopted for the purposes of the transportation assessment will be those as described in Section 3.  In particular, the critical sections are as follows:

·           Blades at up to 30m long and 5 tonnes in weight;

·           Tower sections, up to 4m in diameter, up to 23m long and up to 42 tonnes;

·           Nacelle at up to 12m (L), 4.5m (H), 3.6m (W) and 43 tonnes.

Construction Plant and Equipment:  In addition to the wind turbine components, construction plant and equipment will need to be transported to the Project Site.  The critical item is the crane for the erection of the wind turbine.   A CKE2500 crawler or similar crawler crane will be required to lift the nacelle (up to about 43 tonnes) to the top of the tower (at a height of 60m above ground level). 

Assessment of Options

It is preferred to use the existing access road for the transportation of all the plant and equipment, as far as practicable.   The island currently uses an informal one way system on the existing road network.   To reduce the disturbance to the CSD’s operation on the island, it is preferred to follow the one way system. 

Two alternative routes (see Figure 2.4d) were considered:

·            Long access route where large components are delivered to the existing berthing facility at the north of the island, then transported along the existing road network;

·            Short access route which includes constructing a temporary platform at the existing jetty at the south of the island, and a temporary steel bridge next to the platform.   The plant and equipment will be unloaded from the barge to the temporary platform and then lifted to the deck of the bridge by a mobile crane.  The equipment will then be transported to the Project Site using the existing road.   

Assessment of Alternative Routes

The transport of the large components that make up the wind turbine requires heavy duty transport vehicles and roads that are wide and straight with bends of large radii.  The road along the long route is typically 3m wide and less at some sections with tight bends which cannot accommodate the heavy duty transport without significant impact to slopes, structures and trees.  The width of the transport vehicle itself is 3m and the lower tower sections are even wider than the transport vehicle at up to 4.1m in diameter.  Similarly, the nacelle diameter is up to 4.5m wide and would also be wider than the road and transport vehicle.   The narrow road and tight bends also restricts the length of the vehicle.  The towers sections are up to 23m long and the blades are 30m long and hence would require an extra long heavy transport vehicle and straight roads and bends.  To provide for this the roads have to be widened to provide extra width and to straighten the bends. 

To accommodate the transport of the large turbine components, widening and clearance of trees and structures will generally be required for the whole length of the long access route (about 2.5km).  Therefore the level of impact to environment of slopes, trees and structures is significant.   In addition, the long access route is the main access road to a number of facilities on the island.   Any major road upgrading works will have significant impacts on the CSD’s operation on the island.  

Transporting wind turbine components, especially the tower sections by the long access route, is not preferred as this option will have a significant impact on the existing road network, local environment and CSD’s operation. 

The short access route is the preferred route for transporting the wind turbine components (ie nacelle, blades and steel tower sections) as it will only involve construction of a temporary platform, a bridge and minor road upgrading works.    The impacted areas due to construction of the footings of the temporary bridge (about 5m x 5m each) are small.  However, in order to construct the short access route and lift the wind turbine components from the temporary platform to the deck of the bridge, it is necessary to deliver a mobile crane and a self-propelled transporter using the existing long access route.   It is therefore still required to upgrade the some sections of the existing long access route for the transportation of these equipments. 

The degree of enabling works (in terms of the number and extent of slope works) along the long access route will be significantly reduced if a combination of the long and short access routes are adopted.    

Taking account of the engineering feasibility and the need to minimise the potential environmental impacts associated with the road upgrading works, the best access option will therefore be the use of:

(a)        the long access route to deliver the general construction plant and equipment, and construction workers; and

(b)       the short access route to unload and transport the wind turbine components.  

2.5                            Consideration of Alternative Aviation Warning Marking Schemes

As discussed in Section 2.3, there is a helicopter landing site “CC03” that is used by the GFS at the north of the Project Site.     Although the Project Site location is outside the approach and exit zones of the helicopter flight path for this landing site, the Project site is located in proximity to the helicopter landing site “CC03” and the Hong Kong - Macau helicopter route A (see Figure 2.2ae), thus, CAD requires that the wind turbine be provided with suitable lighting and markings (alternative orange and white bands).    The marking will alert the helicopter pilot the presence of the wind turbine but will also increase its visual intrusion. 

A number of marking schemes (see Figure 2.5a) were developed which aim to provide the necessary warning to the pilot but also to make it less visual intrusive.   A number of Government departments were consulted, including EPD, Planning Department and CAD to assess the alternatives.

When analysing the visibility of the marking schemes, it is clear that Option 1 would have the highest visibility, with Option 6 and 8 having the lowest visibility.  Consultations with CAD indicated that only Options 1 to 3 would be acceptable.  As the hub and nacelle represents the largest visible elements from a distance, no marking on these elements is desirable.

Therefore in order to reduce the impact of the markings, Option 3 was chosen as there are no markings on the nacelle, as shown in Option 2, and the hub of the blades is also unmarked, as shown in Option 1.    The consultation resolved that Option 3 is the least visually intrusive marking scheme while satisfying the aviation safety requirements of CAD.



 

([1])    For the purpose of a pilot demonstration to satisfy the objectives as described in Section 1.1, it is not considered appropriate to develop an off-shore wind turbine which requires the construction a new submarine cable connecting the wind turbine and CLP’s supply gird.

([2])    The strategic and district planning criteria considered included:  (a) whether plans (ie OZP/ODP) are available indicating that the site is designated/intended for development that is incompatible with the wind turbine; and (b) weather strategic (non-statutory) plans are available indicating that the site is designated/intended for development that is incompatible with the wind turbine, eg recreation zones, conservation area and certain use’s under the Hong Kong’s SAR Government studies.

([3])     This is related to potential hazard to existing /committed commercial or residential developments due to fallen object (ie blades) from the turbine.  The potential sites were evaluated based on the distance from developments.

([4])     These criteria were selected to cover a range of environmental, planning and engineering issues that are directly relevant to the suitability of a site for a wind turbine pilot demonstration.  Two key environmental parameters (including conservation importance which covers the potential impacts on importance ecological habitats and wildlife, and noise are considered most relevant with respect to broad screening of the potential areas.      

([5])    It covers air, noise, ecology, water quality, waste, landscape and visual, and cultural heritage considerations.