Galloper Wind Farm Project - Galloper Wind Farm proposal
Galloper Wind Farm Project - Galloper Wind Farm proposal
Galloper Wind Farm Project - Galloper Wind Farm proposal
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<strong>Galloper</strong> <strong>Wind</strong> <strong>Farm</strong> <strong>Project</strong><br />
Preliminary Environmental Report – Chapter 6: <strong>Project</strong><br />
Details<br />
<strong>Galloper</strong> <strong>Wind</strong> <strong>Farm</strong> Limited
Document title <strong>Galloper</strong> <strong>Wind</strong> <strong>Farm</strong> <strong>Project</strong><br />
Preliminary Environmental Report – Chapter<br />
6: <strong>Project</strong> Details<br />
Document short title <strong>Galloper</strong> <strong>Wind</strong> <strong>Farm</strong> PER<br />
Status Final Report<br />
Date 3 June 2011<br />
<strong>Project</strong> name <strong>Galloper</strong> <strong>Wind</strong> <strong>Farm</strong> <strong>Project</strong><br />
Client <strong>Galloper</strong> <strong>Wind</strong> <strong>Farm</strong> Limited<br />
Reference 9V3083/R01/303424/Exet<br />
Drafted by Peter Gaches, Jon Allen et al.<br />
Checked by Rob Staniland, Peter Thornton<br />
Date/initials check RS PT 30.05.2011<br />
Approved by Dr. Martin Budd (Royal Haskoning)<br />
Date/initials approval MB 30.05.2011<br />
GWFL Approved by Kate Tibble (GWFL)<br />
Date/initials approval KT 1.06.2011<br />
A COMPANY OF<br />
<strong>Galloper</strong> <strong>Wind</strong> <strong>Farm</strong> PER - i - 9V3083/R01/303424/Exet<br />
Final Report 3 June 2011
CONTENTS<br />
Page<br />
6 PROJECT DESCRIPTION 1<br />
6.1 Introduction 1<br />
6.2 Outline <strong>Project</strong> Description 1<br />
6.3 Site Location 1<br />
6.4 <strong>Wind</strong> Resource 2<br />
6.5 Offshore Physical Characteristics 3<br />
6.6 <strong>Wind</strong> <strong>Farm</strong> Layout Options 4<br />
6.7 Foundation Systems 9<br />
6.8 WTG Support Structures 29<br />
6.9 WTG Support Structure Ancillary Equipment 32<br />
6.10 <strong>Wind</strong> Turbine Generators 34<br />
6.11 Ancillary Infrastructure 39<br />
6.12 Inter, Intra-array and Export Cables 42<br />
6.13 Cable Landfall and HDD Works 53<br />
6.14 Onshore Transition Pits 57<br />
6.15 Onshore Cabling 58<br />
6.16 Onshore Substation 61<br />
6.17 <strong>Project</strong> Programme 70<br />
6.18 Offshore Pre-construction and Construction 72<br />
6.19 Onshore Construction 75<br />
6.20 Commissioning 78<br />
6.21 Offshore Operations and Maintenance 79<br />
6.22 Onshore Operations and Maintenance 83<br />
6.23 Repowering 85<br />
6.24 Decommissioning 86<br />
6.25 References 87<br />
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6 PROJECT DESCRIPTION<br />
6.1 Introduction<br />
6.1.1 This Chapter presents the details of the <strong>Galloper</strong> <strong>Wind</strong> <strong>Farm</strong> (GWF) scheme<br />
and describes the construction, operation, maintenance and<br />
decommissioning components of the project, which would primarily comprise:<br />
� <strong>Wind</strong> turbine generators (WTG) and supporting tower structures;<br />
� WTG foundations with associated support and access structures;<br />
� Offshore platforms to support offshore substation(s), collection station<br />
and potentially accommodation facilities;<br />
� Meteorological mast(s);<br />
� Subsea inter and intra-array and export cables;<br />
� Cable landfall;<br />
� Onshore transition pits;<br />
� Onshore cabling from the landfall to the GWF substation;<br />
� Horizontal Directional Drilling (HDD) under two roads and across<br />
foreshore habitats;<br />
� 132kV onshore GWF compound and 132kV/400kV onshore<br />
transmission compound, which together are referred to as the “GWF<br />
substation”;<br />
� Onshore cabling from the 132kV/400kV transmission compound to the<br />
sealing end compounds;<br />
� Transmission sealing end compounds adjacent to existing electricity<br />
transmission towers (pylons); and overhead line connections to the<br />
towers;<br />
� Alterations to existing electricity transmission towers;<br />
� Temporary works and laydown areas;<br />
� Permanent and temporary access roads; and<br />
� Onshore cabling from the 132kV/400kV transmission compound<br />
connecting into the existing Greater Gabbard Offshore <strong>Wind</strong> <strong>Farm</strong><br />
(GGOWF) 132kV cables (which run from Sizewell B to the GGOWF<br />
substation).<br />
The diagram on the following page shows the high level components of<br />
<strong>Galloper</strong> <strong>Wind</strong> <strong>Farm</strong>.<br />
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6.1.2 The details provided below are based on the latest knowledge and<br />
information available at the time of production of the Preliminary<br />
Environmental Report (PER). In some cases, specific information relating to<br />
GWF is not available (for example, the exact method of construction will not<br />
be confirmed until contracts have been tendered and appointed). As such,<br />
construction methodology provided herein is based on similar projects.<br />
Complex and extensive detailed design and procurement processes take<br />
place over a lengthy period closer to construction on a scheme of this scale.<br />
6.1.3 For the purposes of the consent documentation, <strong>Galloper</strong> <strong>Wind</strong> <strong>Farm</strong> Limited<br />
(GWFL) will therefore provide a range of possible options with regard to<br />
certain aspects of construction methodology and project components. GWFL<br />
has provided sufficient flexibility in this project description to ensure that all<br />
realistic development scenarios are captured within this Preliminary<br />
Environmental Report (PER). Furthermore, it is noted that the design<br />
information provided is representative of the maximum scenario (in terms of<br />
size, number, depth etc). These two facets serve to ensure that consultees<br />
can have confidence that the initial assessments made within the PER will be<br />
on a scenario that represents the upper limit (or realistic worst case) of what<br />
may actually take place (as discussed in Chapter 5 EIA Process). It is<br />
noted, that whilst these upper ranges have been assessed, in the final design<br />
GWFL may seek to develop less than these maximum values.<br />
6.2 Outline <strong>Project</strong> Description<br />
6.2.1 As outlined in Chapter 1, the GWF project comprises a development of up to<br />
140 WTG, with a maximum capacity of up to 504MW encompassing an area<br />
of 183km 2 comprising up to three distinctly identifiable areas and inter-array<br />
cabling (Development Areas A, B and C – see Figure 1.1 in Chapter 1).<br />
6.2.2 Detail of the specific project components currently under consideration are<br />
provided throughout this Chapter, along with descriptive information on the<br />
methods associated with the construction, operation and decommissioning of<br />
these components. This information has been used to inform the technical<br />
chapters contained within this PER and is considered to represent the<br />
<strong>Project</strong>’s ‘consent envelope’.<br />
6.2.3 The technical elements of the <strong>Project</strong> give rise to the potential for multiple<br />
options in accordance with the <strong>Project</strong> design parameters (e.g. for WTGs and<br />
foundations). The implications for the PER are discussed within Chapter 5<br />
under the Rochdale Envelope principle.<br />
6.3 Site Location<br />
6.3.1 Located approximately 27km off the Suffolk coast, at the nearest point, the<br />
GWF project lies immediately adjacent to the existing Greater Gabbard<br />
Offshore <strong>Wind</strong> <strong>Farm</strong> (GGOWF) project (see Figure 1.1 in Chapter 1).<br />
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6.3.2 The export cable corridor would connect from the offshore development to a<br />
landfall south of Sizewell on the Suffolk coast, adjacent to the route of the<br />
existing GGOWF export cables. The corridor shown in Figure 1.1 shows the<br />
export carroidor to the North of GGOWF, but the export cables will come into<br />
shore in the GGOWF export cable corridor.<br />
6.3.3 The onshore GWF substation would comprise a new GWF 132kV compound<br />
and also a new 132kV/400kV transmission compound, as described in 6.1.1.<br />
The two compounds would be located alongside each other and together are<br />
referred to as the GWF substation.<br />
6.3.4 The GWF substation is located near Sizewell, approximately 1km inland on<br />
the Suffolk coast. It would be situated to the north of Sizewell Gap,<br />
immediately to the west of the existing GGOWF substation site (see Figure<br />
1.2 in Chapter 1).<br />
The onshore transition pit(s) would be located in land to the south of Sizewell<br />
Gap with onshore cabling from there to the proposed GWF substation. There<br />
would be a need for additional cabling between the transmission compound<br />
and the sealing end compounds and also between the transmission<br />
compound and the existing GGOWF cables (see Figure 1.2).<br />
6.4 <strong>Wind</strong> Resource<br />
6.4.1 To minimise initial intrusive works, it was established that the current<br />
meteorological mast located on the GGOWF site (4km from the western tip of<br />
GWF Area A) presented current and historic data which would be<br />
representative of the GWF site.<br />
6.4.2 The first measurements were recorded by the mast in August 2005. The<br />
mast continues to collect data and to date has recorded over five years of<br />
data. Measurements are at a range of heights between 42.5m and 86m<br />
above mean sea level (amsl).<br />
6.4.3 Using the data set from August 2005 to July 2010, a mean wind speed of<br />
9.4m/s was calculated at 86m amsl (which is indicative of conditions at hub<br />
height), using the mean of monthly means method to account for seasonal<br />
variation.<br />
6.4.4 <strong>Wind</strong> direction over this period was predominantly from the southwest (Plate<br />
6.1).<br />
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Plate 6.1 Long term wind rose for GGOWF and GWF<br />
6.5 Offshore Physical Characteristics<br />
6.5.1 GWFL has developed a sound appreciation of the physical conditions<br />
(bathymetry, seabed sediments and shallow geology) of the GWF site. This<br />
has been achieved by site investigations including a geophysical survey<br />
campaign and utilising the detailed knowledge gained from developing the<br />
adjacent GGOWF project. Chapter 10 provides a detailed account of these<br />
physical parameters.<br />
6.5.2 The data is sufficiently detailed to enable GWFL to have confidence that the<br />
conditions present are conducive to the development of an offshore wind<br />
farm and associated cable infrastructure. Water depths vary significantly<br />
across the development area which would give rise to consideration of<br />
multiple foundation solutions to accommodate different depths, turbine types<br />
and ground conditions as presented in Section 6.7.<br />
6.5.3 The Outer Gabbard Bank (an open shelf linear tidal sand bank) is present<br />
within Area A (see Figure 1.1 in Chapter 1 Introduction). The sand bank<br />
would be avoided for environmental reasons. The presence of<br />
Paeolochannels (see Chapter 10) may also have a bearing on the final<br />
layout of the WTGs within Development Areas A, B and C.<br />
The current level of information is sufficiently detailed to enable a robust EIA<br />
to be undertaken. However, additional survey will be required to facilitate<br />
final detailed design in key areas including:<br />
� For foundation structures and scour protection (if required);<br />
� Subsea cables within the wind farm site and along the export cable<br />
route; and<br />
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� Any jack-up vessel operations (vessels with legs that can be lowered<br />
to the seabed allowing the hull of the vessel to be raised clear above<br />
the water).<br />
6.5.4 With the adoption of a Front End Engineering Design (FEED) approach it is<br />
anticipated that these investigations would be conducted prior to the start of<br />
construction and would include:<br />
� Boreholes at a select number of foundation locations and along the<br />
export cable route;<br />
� Cone penetrometer testing (CPT) at a select number of foundation<br />
locations and along the export cable route;<br />
� Vibrocore sampling along the export cable route;<br />
� Plough trials along the export cable route;<br />
� Pre-lay grapnel runs along the export cable route;<br />
� Unexploded Ordnance (UXO) survey; and<br />
� Investigation of any obstructions to construction that are identified<br />
through geophysical survey.<br />
6.5.5 Geotechnical investigations both within the wind farm site and cabling areas<br />
would be to a depth below the design penetration depth of the foundation<br />
options and potential cable burial depths to give confidence in results, design<br />
and construction approach<br />
6.5.6 Geophysical survey investigations would be carried out in accordance with<br />
relevant Maritime and Coastguard Agency (MCA) guidance (MGN 371) and<br />
International Hydrographic Organisation (IHO) standards (IHO Order 1a) and<br />
encompass the project footprint. Further pre-construction survey may<br />
include further higher coverage (200%) multibeam surveys around each<br />
foundation location followed by a Remotely Operated Vehicle (ROV)<br />
inspection if anything relevant for UXO assessment is identified. Ultrasonic<br />
investigations and acoustic coring local to foundation locations would be<br />
undertaken for scour assessment.<br />
6.5.7 Further detail of this pre-construction activity (in terms of vessel types and<br />
durations) is provided in Section 6.19.<br />
6.6 <strong>Wind</strong> <strong>Farm</strong> Layout Options<br />
6.6.1 The maximum turbine population of the wind farm for any given turbine size<br />
would be primarily driven by optimising the space between WTGs to gain<br />
maximum effect from the wind resource. In the prevailing wind direction, the<br />
WTGs would be spaced at a minimum of 8 rotor diameters apart. At 90<br />
degrees to the prevailing wind the WTGs would be spaced at a minimum of 6<br />
rotor diameters apart (termed as an 8 by 6 grid).<br />
6.6.2 WTGs generating capacity is driven by their swept area (determined by blade<br />
length) and internal generating components. Hence turbines of the same<br />
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otor diameter may not have the same MW capacity. The WTG under<br />
consideration (Table 6.4 later in this document) in this PER range from 107m<br />
to 164m rotor diameter and hub height 79m to 120m. These have different<br />
technical and dimensional characteristics but the site would not incorporate<br />
any more than 140 WTGs nor have a greater total output than 504MW.<br />
6.6.3 Example indicative layouts to show how rotor diameters of 107m, 120m and<br />
150m might be laid out across the site area are presented in Figures 6.1 to<br />
6.3. These layouts are based on the physical, environmental and human<br />
information obtained for the site to date and take into account the known<br />
constraints posed by these parameters. These indicative layouts have been<br />
used to inform the relevant studies carried out within the EIA for the GWF<br />
project. Parameters which are used to influence layouts include:<br />
� Water depths;<br />
� Seabed geology;<br />
� Ship wrecks and other obstructions;<br />
� <strong>Wind</strong> resource assessment;<br />
� Ornithological recommendations;<br />
� Stakeholder feedback;<br />
� Proximity to the future East Anglia Offshore <strong>Wind</strong> <strong>Farm</strong>s; and<br />
� Proximity to the existing GGOWF.<br />
6.6.4 As a result of the above the final layout would not be fixed until FEED work<br />
and tendering has been completed post consent. Therefore these layouts<br />
represent reference layouts that may be used when considering the multiple<br />
variations available.<br />
6.6.5 In practice, it is unlikely that any of these indicative layouts would be<br />
constructed exactly as shown in Figures 6.1 to 6.3, as the necessary<br />
detailed work post-consent will inevitably produce a different layout. The<br />
Development Consent Order will not contain any layout plans for the offshore<br />
infrastructure, simply the red line areas within which the infrastructure can be<br />
built, together with various restrictions (maximum number of turbines,<br />
maximum height etc).<br />
6.6.6 The final built layout will not necessarily be evenly spread across entire<br />
development areas. Also, not all of the development areas will necessarily<br />
be used, for example Area C. This is discussed in more detail in Chapter 5<br />
EIA Process.<br />
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6.7 Foundation Systems<br />
6.7.1 There are four foundation options under consideration for supporting the<br />
WTG structures; monopiles, space-frame structures (Jacket/Tripod), gravity<br />
base structures (GBS) and monopod suction-buckets. The requirement for<br />
this level of flexibility in options is principally driven by the large variation in<br />
water depths across the site, differing geological conditions across the site<br />
and potential for use of different turbine types.<br />
6.7.2 Given the varying site factors it is possible that multiple foundation solutions<br />
would be utilised to address commercial uncertainty on the project.<br />
6.7.3 Determination on the final foundation type or types to be used for the project<br />
would be made following FEED work post consent. Consideration would be<br />
given to:<br />
� Assessment of foundation impact on receiving environment;<br />
� Geological profile of the seabed;<br />
� Water depth;<br />
� Geotechnical properties of soil;<br />
� Site metocean conditions (wind, wave, current and tidal regime);<br />
� WTG selection;<br />
� Access and maintenance requirements;<br />
� Foundation material, fabrication, transportation and installation costs;<br />
and<br />
� Availability of foundation supply chain components (apparatus / lifting<br />
vessels etc).<br />
6.7.4 The following sections provide an overview of the different foundation options<br />
under consideration together with their typical installation process.<br />
Furthermore, for each foundation type, discussion is provided on the<br />
situations in which each option might be deployed to enable a realistic worst<br />
case scenario to be developed for the EIA (see Chapter 5 EIA Process).<br />
Monopile foundations<br />
The assessments presented in the PER are on the basis of monopiles in water depths<br />
of up to 35m. At the time of writing GWF are also considering the possibility of using<br />
monopiles in up to 45m water depth. This is likely to represent the ‘worst case’ for<br />
assessments relating to underwater noise impact (for example, those detailed in<br />
Chapter 14 – Fish and Shellfish Resource and Chapter 15 – Marine Mammals). The<br />
PER, as written, has assumed a maximum water depth of up to 35m for monopiles.<br />
The final submitted ES will include assessments based on up to 45m.<br />
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General overview<br />
6.7.5 Monopile foundation systems have been the mainstay of the UK offshore<br />
wind industry to date and are the foundation solution that has been adopted<br />
for the adjacent GGOWF project.<br />
6.7.6 Monopile foundations (Plate 6.2) comprise a single, large diameter hollow<br />
steel pile that relies on the soil to provide lateral resistance to loading. A<br />
separate Transition Piece (TP) would be installed on top of the monopile to<br />
provide a horizontal levelled platform for the WTG structure support. The TP<br />
would be lifted onto the monopile and a grout injected into the interface to<br />
bond the TP to the monopile structure.<br />
6.7.7 The size (diameter and length) of the monopile depends upon the water<br />
depth, metocean conditions and ground conditions as well as the size of<br />
WTG that it supports. Based on the current knowledge of physical conditions<br />
at the GWF site and experience from the adjacent GGOWF project, GWFL<br />
consider that the WTG options under consideration would have a maximum<br />
size of monopile of 7m in diameter by 90m in length.<br />
Plate 6.2 Indicative monopile foundation<br />
Work<br />
platform<br />
Intermediate<br />
platform<br />
External<br />
J tubes<br />
Grouted<br />
connection<br />
Scour protection<br />
(if required)<br />
Turbine tower<br />
Boat landing<br />
/ ladder<br />
Transition piece<br />
Monopile<br />
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Installation process<br />
6.7.8 Installation of monopiles would be carried out using a dedicated heavy lift<br />
vessel (HLV) or a jack-up barge.<br />
6.7.9 A crane would be used on the installation vessel/jack-up barge to manoeuvre<br />
the monopile into a guide frame that supports the monopile during the<br />
installation process (see Plate 6.3).<br />
Plate 6.3 Monopile installation<br />
Source: GGOWL, 2011<br />
6.7.10 There are two methods of installation for the monopile that are considered to<br />
be applicable for GWF:<br />
� Driven to full penetration; and<br />
� Drive / drill / drive.<br />
Driven to full penetration<br />
6.7.11 The driven method initially allows the pile to sink under its own weight and<br />
then the required penetration depth into the seabed would be achieved using<br />
a hydraulic hammer installed on top of the monopile as depicted in Plate 6.4.<br />
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Plate 6.4 Monopile driven installation<br />
Source: GGOWL 2011<br />
Drive / drill / drive<br />
6.7.12 The monopile would be sunk under its own weight, and then driven into the<br />
seabed using a hydraulic hammer until a pre-determined refusal point is<br />
reached. The first refusal would be gauged by the blow count and travel of<br />
the pile. The pile hammer would be then removed and a drilling rig system<br />
would be installed within the monopile.<br />
6.7.13 The drill continues down to a location typically 0.5m above the final design<br />
elevation of the toe of the monopile. The drilling rig would then be removed<br />
and the pile hammer placed on the monopile once again. The monopile<br />
would then be driven into the drilled cavity until the required penetration is<br />
obtained.<br />
6.7.14 The cutting action of the drill would create spoil or ‘arisings’. These arisings<br />
would be lifted from inside the monopile by using a suction pump unit. The<br />
arisings would then deposited and left in-situ on the seabed around the<br />
monopile.<br />
Deployment philosophy<br />
6.7.15 As detailed in Table 6.1, GWFL’s assumption based on site conditions and<br />
previous experience is that GWF would promote the deployment of<br />
monopiles in water depths up to - 45mb LAT.<br />
6.7.16 Up to two piling vessels and rigs may be present and operational at the site<br />
at any one time.<br />
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Gravity base structure foundations<br />
General overview<br />
6.7.17 Gravity Base Structure (GBS) foundations are typically constructed in steel or<br />
concrete and use their weight to remain stable on the seabed. The GBS<br />
foundation holds position on the seabed through frictional forces, which is<br />
often enhanced by the provision of grout under the base of the structure and<br />
skirts around the structure’s perimeter. These skirts (see Plates 6.5 and 6.6)<br />
move the friction plane downwards from the relatively weak surficial<br />
sediments into a stronger undisturbed soil layer below. The skirts also serve<br />
to ensure that any scour that may occur around the perimeter does not<br />
undermine the structure.<br />
6.7.18 GBS foundations would either be conical or column based in shape, as<br />
depicted in Plates 6.5 and 6.6. Maximum dimensions for these structures<br />
are provided in Table 6.1.<br />
6.7.19 GBS foundations are used extensively in European Offshore <strong>Wind</strong>farms<br />
(such as Vindeby, Middelgrunden and Nysted in Denmark). GBS<br />
foundations are foreseen as part of a diverse foundation supply chain<br />
required to meet the offshore wind industry’s contribution to UK government’s<br />
renewable energy targets.<br />
6.7.20 The GBS foundations will have a transition structure, (see Section 6.8),<br />
which would be an integrated part of the foundation and upon which the<br />
tower would be mounted. This could be a flanged bolted connection.<br />
Plate 6.5 Indicative conical GBS foundation<br />
Intermediate<br />
Platform<br />
Work Platform<br />
Boat Landing / Ladder<br />
Skirt<br />
Under-base Grout<br />
Shaft<br />
Turbine<br />
Tower<br />
Internal J-tube &<br />
Ballast<br />
Scour Protection<br />
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Plate 6.6 Indicative column GBS foundation<br />
Work<br />
Platform<br />
Intermediate<br />
Platform<br />
External J-tubes<br />
Skirt<br />
Turbine<br />
Tower<br />
Boat Landing<br />
Shaft<br />
Scour protection<br />
Under-base<br />
grout<br />
Installation process<br />
6.7.21 GBS foundations may require a degree of seabed preparation prior to their<br />
installation to ensure they are laid on a surface capable of supporting the<br />
structure adequately. Grout is used to help bond the foundation base to the<br />
seabed. The maximum volume of grout used in this process would be<br />
estimated at approximately 1,590m 3 per foundation.<br />
6.7.22 Should seabed preparation be required, a maximum of 2m in thickness of<br />
material (2,000m 3 ) would be removed from the seabed at the location of each<br />
foundation. Inert levelling material (comprising stone or aggregate) would<br />
then be deposited in place prior to installation of the foundation.<br />
6.7.23 The arisings produced from the seabed levelling (achieved through dredging)<br />
would be disposed of in-situ. The arisings likely to be produced from the<br />
seabed preparation for GBS foundations comprise deposits of sand and<br />
gravel with occasional potential for London clay where present close to the<br />
surface.<br />
6.7.24 The GBS foundations can either be transported to site on a dedicated barge<br />
or as a self floating tow.<br />
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6.7.25 Installation would typically be undertaken through the use of a heavy lift<br />
vessel where the gravity base is lowered on to the prepared seabed, or if<br />
floated to site under their own buoyancy, then ballasted onto the seabed<br />
using tug-boats to control operations. Material used to ballast the foundation<br />
would typically comprise rock, gravel, shingle or sand (depending on the<br />
weight required).<br />
6.7.26 Following deployment of the GBS, a fall pipe vessel would install scour<br />
protection about the base of the foundation to prevent seabed scour about<br />
the base of the structure (a maximum of 1,600m 3 per foundation).<br />
Deployment philosophy<br />
6.7.27 As detailed in Table 6.1, GBS may be deployed in water depths up to -45mb<br />
LAT where ground conditions are suitable.<br />
Plate 6.7 Indicative GBS installation process<br />
Space-frame foundations<br />
General overview<br />
6.7.28 Space-frame foundations encompass structures that are commonly lattice<br />
type or consist of main legs and braces. The most common space-frame<br />
structure is a space frame (jacket) foundation that has been widely deployed<br />
to successfully support offshore oil and gas platforms. Tripods are a<br />
monopile/space frame hybrid in which a large central column is supported at<br />
its base by a frame piled at its 3 corners.<br />
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6.7.29 This system is used to support WTGs in deeper water (typically greater than -<br />
45mb LAT) or to support heavier WTGs i.e. 5MW to 7MW class. Spaceframes<br />
are generally stiffer than a monopile and more transparent to wave<br />
loading. Space-frames are typically installed without scour protection given<br />
their small pile dimensions and therefore have low influence on tidal and<br />
wave induced currents.<br />
6.7.30 The space-frame consists of a steel frame with slender leg members<br />
(typically four legs but three legs would also possible), with steel cross<br />
bracings. The members are steel tubes with bracings and would be prefabricated<br />
onshore. The space frame can be attached to the seabed by long<br />
cylindrical piles approximately 40m to 60m in length. Plate 6.8 shows a four<br />
leg post piled space frame structure. Suction cans may also be used under<br />
the leg of each support structure, resisting force by friction and active suction<br />
with the seabed. They are normally made of steel, cylindrical, have a closed<br />
top and are typically approximately 10m in diameter. Plate 6.9 shows the<br />
indicative suction can substructure.<br />
6.7.31 The transition structure for space-frame foundations would be an integrated<br />
component of the foundation as described under GBS.<br />
Plate 6.8 Indicative Space frame lattice substructure<br />
Work<br />
External J-<br />
Pile<br />
Transition<br />
Tower<br />
Central column<br />
Intermediate<br />
Boat landing<br />
Mud mats<br />
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Pin
Plate 6.9 Indicative suction can substructure<br />
Installation process<br />
6.7.32 A degree of seabed levelling may be required prior to the installation of the<br />
space-frame and this would be undertaken using dredging equipment with<br />
high resolution sonar to ensure that the seabed level is within the required<br />
tolerances after the intervention works and prior to the installation of the<br />
space frame. The maximum volume of arisings per turbine depending on<br />
local conditions is detailed in Table 6.1.<br />
6.7.33 Installation is usually carried out using a dedicated HLV or a jack-up barge<br />
(as detailed for monopiles). However, as this option is very much in a<br />
development phase it is highly possible that a combination of vessels would<br />
be used.<br />
6.7.34 The installation process for this system would be expected to take up to one<br />
day dependent on the number of legs associated with the space-frame<br />
foundation.<br />
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Plate 6.10 Installation of tripod structure from HLV<br />
6.7.35 There are two options for the installation of the cylindrical pin piles for a<br />
space-frame structure. The pins are significantly smaller diameter than those<br />
used for the monopile concept (Table 6.1). For pre-piled space-frame<br />
solutions, pin piles may be installed prior to the space-frame, with the<br />
foundation then lowered onto the piles with the legs being inserted into the<br />
piles (Plate 6.11). Alternatively, the foundation would be placed onto the<br />
seabed and the piles driven through sleeves connected to the space-frame<br />
legs, as shown in Plate 6.12. Installation of suction can piles would be<br />
carried out using a jack-up barge or similar, that lifts and places them onto<br />
the seabed. Pumps would be connected to the suction cans and operated<br />
until the can ‘lid’ is flush with the seabed. Multipile suction can foundations<br />
may require rock ballast to meet design requirements.<br />
6.7.36 In both designs, the piles would be typically attached to the foundation by a<br />
grouted connection, although other appropriate connections may be used.<br />
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Plate 6.11 Indicative pre-installed pile space-frame option<br />
Plate 6.12 Indicative driven pile space-frame option<br />
Side view of the spaceframe<br />
foundation on the<br />
seabed prior to the<br />
piles being driven in<br />
Driving Piles<br />
Space-frame foundation with<br />
the piles being driven into the<br />
seabed to secure the structure<br />
Deployment philosophy<br />
6.7.37 As detailed in Table 6.1, space-frame systems can be deployed in any water<br />
depths across the site where ground conditions are suitable.<br />
6.7.38 The maximum number of piles installed with a space-frame foundation<br />
system at any one time would be two.<br />
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Monopod suction-bucket foundations<br />
General overview<br />
6.7.39 Suction-buckets are tubular steel foundations that utilise the hydrostatic<br />
pressure difference and their deadweight to enable the bucket to penetrate<br />
the soil. This installation procedure allows the buckets to be connected to<br />
the rest of the structure before installation, enabling a reduction in the<br />
number of steps to the installation procedure. The system has been tried in<br />
practice in the Norwegian oil and gas fields in the North Sea (DOWEC, 2003)<br />
as well as at Horns Rev 2 offshore wind farm for the met mast foundation<br />
(see Plate 6.13).<br />
Plate 6.13 A typical suction-bucket foundation<br />
Source: DONGenergy (2009)<br />
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Installation process<br />
6.7.40 Suction monopods may be floated to site under their own buoyancy using<br />
tug-boats or transported on a dedicated barge. Installation would be carried<br />
out using a dedicated HLV or a jack-up barge that lifts the monopod into the<br />
upright position and positions it onto the sea-bed. Pumps would be<br />
connected to the suction caisson and the ‘bucket’ penetrates into the seabed<br />
until the top surface of the base is flush with the seabed. Small volumes of<br />
seabed sediment may be extracted and deposited locally during this process.<br />
Deployment philosophy<br />
6.7.41 Suction-bucket foundations can be installed into water depths up to -45mb<br />
LAT. The maximum number of foundations installed at any one time would<br />
be two.<br />
Foundation detail summary<br />
Table 6.1 Summary of foundation parameters<br />
Foundation detail Monopiles Gravity<br />
base<br />
systems<br />
Space-Frame<br />
(tripod / jacket)<br />
Suction<br />
buckets<br />
Maximum water depth 45m 45m >45m 45m<br />
Maximum diameter at seabed 7m 45m 3m per pile 25m<br />
Column diameter 7m 10m N/A 9m<br />
Maximum No piles per<br />
foundation<br />
Maximum seabed footprint<br />
(per foundation)<br />
1 None Space frame: 8<br />
(2 piles per leg,<br />
up to 4 legs)<br />
38.5m 2<br />
Maximum No. legs 1 1<br />
1,590m 2 Space frame:<br />
57m 2 (7.1m 2 *8)<br />
Space frame: 4 1<br />
None<br />
490m 2<br />
Maximum penetration depth 50m 5m 70m 20m<br />
Maximum number of piling<br />
driven at any one time<br />
Maximum volume of grout (per<br />
foundation)<br />
Maximum volume of arisings<br />
(per foundation)<br />
1 None 2 None<br />
23m 3 1,590m 3 188m 3 N/A<br />
1,600m 3<br />
7,200m 3 1,300m 3 500m 3<br />
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Table 6.2 Foundation build-out scenarios<br />
Build-out scenarios – Foundations<br />
Single foundation type (A)<br />
Single foundation type (B)<br />
Mixed foundation type<br />
Optimised smaller project on monopiles in<br />
shallow water<br />
<strong>Project</strong> on either space frame or suitable<br />
foundation for all water depths<br />
Up to two types of foundation used to<br />
enable development across all water<br />
depths<br />
Fabrication and transportation<br />
At the time of writing, the number of foundation fabrication plants and skilled<br />
labour force, whilst emerging, are still limited within the UK. Therefore such<br />
structures would commonly be brought in from overseas either directly to site<br />
or to a holding port.<br />
6.7.42 If the foundations are shipped to a holding port, there are two principal<br />
methods for transporting the foundations to their installation location:<br />
� Floating transportation procedure; or<br />
� Direct lift procedure.<br />
6.7.43 Floating transportation procedure requires sealing the toe of the pile and<br />
fitting a sealed lifting head at the top of the pile. The sealed lifting head<br />
serves as the towing point. The foundation system would then towed to site<br />
after being lifted into the water using a crane from the holding port key side.<br />
6.7.44 The foundation system would then be upended, using a combination of<br />
controlled ballasting and lifting to ensure stability and positioned in a guiding<br />
or gripper system. These systems are used to guide the foundation system<br />
to the pre-defined location on the seabed whilst maintaining verticality.<br />
6.7.45 The alternative transportation method is the direct lift, where the foundations<br />
are lifted from the quayside onto either a dedicated transportation vessel or<br />
the installation vessel itself, which would be used to transport the foundations<br />
to the offshore location. The foundations would then be lifted from the<br />
transportation vessel by the crane on the installation vessel and pitched into<br />
the installation guiding system.<br />
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Foundation scour protection<br />
6.7.46 Scouring of soft surficial sediments may occur around foundation structures<br />
where localised effects on the hydrodynamic regime take place (see Chapter<br />
10). Such scouring erodes sediment leaving depressions (known as scour<br />
holes or scour tails) around the foundation structures.<br />
6.7.47 Experience from the adjacent GGOWF project, where similar seabed<br />
sediments and hydrodynamic conditions exist, would suggest that scour<br />
events sufficient to require dedicated protection are unlikely to be widespread<br />
(only 5 out of 140, or 3.5% of foundations at GGOWF will have scour<br />
protection installed to date). For the purposes of the GWF project a<br />
conservative approach has been applied to the likely percentages of<br />
foundations that may require scour protection (see Table 6.3).<br />
Table 6.3 Foundation scour detail summary<br />
Foundation detail Monopiles<br />
Maximum scour protection<br />
(radius per foundation/leg<br />
base)<br />
Maximum scour protection<br />
area (per foundation)<br />
Maximum scour protection<br />
depth (per foundation)<br />
Maximum scour protection<br />
volume (per foundation)<br />
Approximate percentage of<br />
foundations requiring scour<br />
protection<br />
Maximum scour protection<br />
volume<br />
50m<br />
Gravity base<br />
systems<br />
Space-frame Suction-<br />
buckets<br />
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10m<br />
1,900m 2 790m 2<br />
2m<br />
3,900m 3 1,600m 3<br />
5%<br />
2m 2m<br />
10m 10m<br />
500m 2<br />
100% 10%<br />
27,300m 3 132,000m 3<br />
450m 2<br />
2m<br />
1,000m 3 950m 3<br />
100%<br />
8,500m 3 80,000m 3
6.7.48 The pre-construction geophysical survey (see Section 6.5) will ascertain the<br />
level of scour protection required for the GWF project. Surveying for any<br />
scour would continue beyond the construction phase of the project and would<br />
form part of the ongoing inspection regime of the wind farm.<br />
6.7.49 Should scour protection be deemed necessary, the following procedure<br />
would typically be adopted:<br />
� A filter layer of gravel would be installed prior to placement of the<br />
foundation<br />
� Rock or slate would be deposited at the base of the foundation<br />
structures after installation of the foundation. The rock placement<br />
would infill any scour pit, which may have developed, as well as<br />
building a profile above the seabed, referred to as a rock berm. The<br />
rock berm would be designed to remain stable for the full life of the<br />
structure under all forms of predicted environmental loading<br />
� The rock or slate would be placed by a vessel using a side tipping<br />
system or placed using a grab device; and<br />
� The base of the structure would be resurveyed to confirm that the<br />
required coverage and rock profile has been achieved.<br />
Foundation installation noise<br />
6.7.50 All marine construction activity generates some level of noise. The<br />
installation of the foundation systems, however, has the potential to generate<br />
significant noise levels. Underwater noise behaves very differently to<br />
airborne noise largely due to the high sound transmission speed within water<br />
(1,500m/s, as opposed to 340m/s for air). Given these considerations<br />
underwater noise is therefore specifically discussed in this Chapter. The<br />
effects of this noise on the sensitive ecological receptors (namely ornithology,<br />
fish and shellfish and marine mammals) are discussed in Chapters 12, 14<br />
and 15 respectively.<br />
6.7.51 The two foundation systems which can be expected to result in the highest<br />
noise levels would be those that have impact piling associated with their<br />
installation, namely monopiles and specific space-frame foundation<br />
structures that use pin piles.<br />
6.7.52 Impact piling involves a large weight or “ram” being dropped or driven onto<br />
the top of the pile, driving it into the ground. Usually double-acting hammers<br />
are used in which compressed air not only lifts the ram, but also imparts a<br />
downward force on the ram, exerting a larger force than would be the case if<br />
it were only dropped under the action of gravity.<br />
6.7.53 Airborne noise would be created by the hammer, partly as a direct result of<br />
the impact of the hammer with the pile. Some of this airborne noise would be<br />
transmitted into the water. Of more significance to the underwater noise,<br />
however, is the direct radiation of noise from the surface of the pile into the<br />
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water as a consequence of the compressional, flexural or other complex<br />
structural waves that travel down the pile following the impact of the hammer<br />
(Subacoustech, in prep). Due to the high transmission properties of sound in<br />
water (1,500m/s, as opposed to 340m/s for air), noise generated from pile<br />
installation will transmit efficiently into the surrounding water column.<br />
Consequently these waterborne sound waves usually provide the greatest<br />
contribution to underwater noise (Subacoustech, In prep).<br />
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6.7.54 At the end of the pile, force would be exerted on the substrate not only by the<br />
mean force transmitted from the hammer by the pile, but also by the<br />
structural waves travelling down the pile inducing lateral waves in the<br />
seabed. These may travel as both compressional waves, in a similar manner<br />
to the sound in the water, or as a seismic wave, where the displacement<br />
travels as Rayleigh waves (Brekhovskikh, 1960). The waves can travel<br />
outwards through the seabed, or by reflection from deeper sediments. As<br />
they propagate, sound will tend to “leak” upwards into the water, contributing<br />
to the waterborne wave. Since the speed of sound is generally greater in<br />
consolidated sediments than in water, these waves usually arrive first as a<br />
precursor to the waterborne wave. Generally, the level of the seismic wave<br />
is 10 to 20 decibels (dB) below the waterborne arrival, and hence it would be<br />
the latter that dominates the noise impact.<br />
6.7.55 Studies carried out to date (Nedwell et al., 2003; Nedwell et al., 2007; Parvin<br />
et al, 2006) indicate that the source level of the noise from impact pile driving<br />
operations is primarily and strongly related to the pile diameter. This<br />
probably results largely from the increased force that is required to drive<br />
larger piles and the improved noise radiation efficiency of larger piles<br />
(Subacoustech, In prep).<br />
6.7.56 For GWF the maximum sized piles considered are 7m in diameter (for<br />
monopiles) and 3m in diameter for space-frame foundations. There is<br />
currently no measured data for piles of 7m diameter, but using extrapolation<br />
from other pile diameters, it is possible to establish indicative noise levels at<br />
GWF piling operations (Subacoustech, In prep).<br />
6.7.57 Sound may be expressed in many different ways depending upon the<br />
particular type of noise, and the parameters of the noise that allow it to be<br />
evaluated in terms of an environmental effect. Those relevant to the GWF<br />
project are described in more detail below:<br />
� Peak to peak level - Usually calculated using the maximum variation<br />
of pressure from positive to negative within the wave. This represents<br />
the maximum change in pressure as the transient pressure wave<br />
propagates. Peak to peak levels of noise are often used to<br />
characterise sound transients from impulsive sources such as<br />
percussive impact piling. Measurements during offshore impact piling<br />
operations are commonly expressed as having a peak to peak source<br />
level of dB’s re 1μPa @ 1m, which describes the noise level<br />
experienced at 1m from the source (Subacoustech In prep).<br />
� Sound Pressure Level (SPL) - Normally used to characterise noise<br />
and vibration of a continuous nature such as drilling, boring,<br />
continuous wave sonar, or background aquatic noise levels. The SPL<br />
method measures the average unweighted level of the sound over the<br />
measurement period (Subacoustech In prep).<br />
� Sound Exposure Level (SEL) - When assessing the noise from<br />
transient sources such as blast waves, impact piling or seismic airgun<br />
noise, characterising the time period of the pressure wave is often<br />
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addressed by measuring the total acoustic energy (energy flux<br />
density) of the wave. Sound Exposure Level (SEL) sums the acoustic<br />
energy over a measurement period, and effectively takes account of<br />
both the SPL of the sound source and the duration the sound is<br />
present in the acoustic environment (Subacoustech In prep).<br />
� M-Weighting – A method used to represent the levels of underwater<br />
noise perceived by marine mammals through filtering underwater<br />
noise data using generalised frequency weighting functions, which are<br />
designed to match the frequency response of different groups of<br />
marine mammals (Subacoustech In prep).<br />
6.7.58 In instances where a single defined noise is emitted underwater, sound<br />
pressure measurements may be expressed using the peak to peak level (i.e.<br />
dB re 1μPa @ 1m), which represents the noise level at a distance of one<br />
metre from the source. The actual level at the source (Source Level) may be<br />
different from that experienced at 1m. The Source Level may be quoted in<br />
any of the measures described above, for a piling source this is typically<br />
expressed as having a “peak to peak Source Level of dB re 1μPa @ 1m”.<br />
6.7.59 Based on this approach it is predicted that noise levels of 254dB re 1 µPa @<br />
1m for 7m diameter piles and approximately 240dB re 1 µPa @ 1m for 3m<br />
diameter piles may be expected for the GWF project (see Plot 6.1). Note<br />
modelling to date has been carried out on 2m pin piles, but approximate<br />
values for 3m piles are drawn from interrogation of the Cubiclaw Fit line (see<br />
Plot 6.1)<br />
Plot 6.1 Predicted noise levels from GWF piling operations (Subacoustech in prep)<br />
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6.7.60 The implications of the noise generated from construction activity on the<br />
receiving environment are assessed and discussed within the relevant<br />
technical Chapters of this report (namely, Chapter 13 Fish and shellfish<br />
resource, and Chapter 14 Marine Mammals).<br />
Foundation corrosion protection<br />
6.7.61 Any offshore metal structure (typicall steel), below the water level or in the<br />
splash zone will corrode freely without corrosion protection. Corrosion can<br />
reduce the structural integrity of the WTG support structure, hence corrosion<br />
protection is required. The design of the internal and external corrosion<br />
protection systems (CPS) utilised at GWF will be agreed with the Certification<br />
Bodies, namely Det Norske Veritas (DNV), Germanischer Lloyd (GL) or<br />
Lloyds Register, who will be responsible for certifying the subsea structure.<br />
Internal corrosion protection<br />
6.7.62 Internal corrosion prevention measures are required in subsea foundation<br />
types comprised of steel (i.e. all excluding concrete GBS foundations) as a<br />
result of the sea water that would be trapped inside the structures after<br />
installation. Corrosion in this instance would be predominately caused by<br />
microbial activity, both aerobic (with oxygen) and anaerobic (without oxygen)<br />
in nature. Sealing the tops of the foundation structures and removing the<br />
oxygen (by filling the space with an inert gas) would be the primary method to<br />
limit the growth of microbes.<br />
6.7.63 If through investigation the rate of microbial corrosion is deemed to be high,<br />
then additional measures could be undertaken after sampling the sea water<br />
captured in the foundation during the installation process. A biocide could<br />
then be chosen to inhibit the growth of the microbes responsible for<br />
corrosion. However the foundations would be designed to ensure that<br />
biocides do not need to be used initially, although in time internal<br />
investigations and water sampling could identify the need for biocide use.<br />
Biocides are used extensively in the offshore industry to control internal<br />
corrosion. If biocides are used the necessary licences would be sought with<br />
risk assessments and method statements put in place.<br />
External corrosion protection<br />
6.7.64 The external CPS, selected for the TP and foundation would be required to<br />
ensure protection against corrosion and to ensure that the design life of the<br />
project would be met. The external CPS would comprise two primary<br />
systems; an external coating system and a cathodic protection system<br />
provided by one of the following forms:<br />
� Galvanic CP, commonly known referred to as a sacrificial anodes; or<br />
� Impressed current cathodic protection (ICCP).<br />
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6.7.65 The basic principle behind CPS is electrolysis which requires an anode (a<br />
source of negative ions), a cathode (a source of positive ions) and an<br />
electrolyte (a liquid which would conduct the ions, i.e. the sea). A CPS only<br />
operates on the outermost exposed surfaces of the steel structure at the<br />
molecular / atomic level, simplistically a protective force-field to prevent<br />
corrosion.<br />
6.7.66 The Galvanic CP or sacrificial anode system is used heavily in the oil and<br />
gas offshore industry. This system, as the name suggests, uses fixed<br />
anodes, usually zinc, magnesium or aluminium (or alloys of these metals)<br />
placed about the base of the submerged structure which remains there for<br />
the life of the equipment. As the anode is more easily corrodible, there is a<br />
continual electron flow from the anode to the cathode (steel structure)<br />
causing polarisation. The driving force for the CP current flow is the<br />
difference in electrochemical potential between the anode and the cathode.<br />
Galvanic corrosion protections are generally specified to provide adequate<br />
protection for the design life of the foundation. Due to the challenging nature<br />
of Cathodic Protection design, it may be necessary to replace the anodes<br />
within the foundation design life.<br />
6.7.67 The ICCP system is commonly found on boats and submarines. ICCP uses<br />
anodes connected to a directional current (DC) power source; current is<br />
supplied to the anodes causing the cathode (the steel structure) to become<br />
more electronegatively charged and therefore reduces its rate of corrosion.<br />
In this case reference electrodes on the structure are also required to monitor<br />
the electrical potential.<br />
6.8 WTG Support Structures<br />
Transition piece<br />
6.8.1 The TP connects the foundation to the WTG. The TP serves several<br />
different purposes as it can be used to house the necessary electrical and<br />
communication equipment and provide a landing facility for personnel and<br />
equipment from marine vessels.<br />
6.8.2 For space frames and GBS foundations the TP are often integrated to the<br />
foundation and hence discussed in the foundation section. TP are primarily<br />
used for monopiles where the secondary structures cannot be on the<br />
monopole (as it is driven) and, as such, need to be installed on a TP that also<br />
assists verticality via adjustment permitted in the grouted connection.<br />
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Transitional piece: monopile and suction can structures<br />
6.8.3 The TP (Plate 6.14) would be<br />
Plate 6.14 Typical monopile transitional piece<br />
marginally larger in dimensions<br />
than the foundation pile and<br />
would be fitted once the<br />
foundation is in place. The TP<br />
would be craned into position<br />
over the exposed top and<br />
carefully lowered into position.<br />
Once located in situ on top of<br />
the foundation a jack system<br />
would be used to level the TP.<br />
A level top would be essential<br />
as the WTG tower section is<br />
bolted directly onto the TP.<br />
6.8.4 To ensure the TP remains in the<br />
level position, grout would be<br />
applied between the foundation<br />
and TP to bond the structures<br />
together and provide a load<br />
bearing connection.<br />
6.8.5 The external corrosion<br />
protection system used for the<br />
TP would be as described in<br />
detail for the foundation<br />
systems in Section 6.7.<br />
Source: www.kentishflats.com<br />
Transition piece: space frame structure<br />
6.8.6 The TP associated with a space frame structure (see Plate 6.15) would be<br />
shorter then those used on the other types of foundation structures, primarily<br />
as the space frame structure extends far enough above sea level and would<br />
also be fitted with landing facilities. The TP can be welded into position<br />
onshore prior to the space frame being transported to its offshore location.<br />
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Plate 6.15 Typical space frame transition piece<br />
Transition piece: gravity base structure<br />
6.8.7 A gravity based structure may or may not be designed to accommodate a<br />
TP. If a TP is to be used the design and installation process would be<br />
identical to the monopile TP. It should be noted that if this foundation system<br />
uses a TP then less seabed levelling preparation would be required as the<br />
jack system between the GBS and TP can be used to level the top surface.<br />
6.8.8 If no TP is to be used then the GBS would extend further above the sea level<br />
and require landing facilities and auxiliary equipment to be installed.<br />
6.8.9 The WTG tower is connected directly onto the GBS structure via a flanged<br />
connection. With this option all the necessary electrical equipment would be<br />
housed within the WTG tower.<br />
Corrosion projection<br />
6.8.10 The corrosion protection utilised for the TP section, is likely to be in line with<br />
that considered for the foundation options.<br />
Electrical equipment<br />
6.8.11 The electrical equipment contained within WTG would typically be housed<br />
within either the TP or the base of the tower (see Section 6.10), and<br />
comprises:<br />
� Converters or power electronics;<br />
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� Low voltage (LV) circuit breakers;<br />
� Transformers (occasionally, for instance a Vestas WTG, would house<br />
the transformer in the nacelle rather than the TP); and<br />
� Medium voltage (MV) circuit breakers.<br />
6.8.12 Cabinets would also be installed to house control equipment, telecoms and<br />
emergency power supply units.<br />
6.8.13 The electrical equipment requires a controlled atmospheric environment,<br />
along with the regulated dissipation of the heat generated. Therefore,<br />
dehumidifiers and air conditioning units would also be installed to ensure a<br />
suitable atmosphere is maintained.<br />
6.8.14 The precise composition of electrical equipment, housing and its location<br />
(within TP or tower) would depend on the WTG selected.<br />
6.9 WTG Support Structure Ancillary Equipment<br />
Introduction<br />
6.9.1 This section details the ancillary equipment that would normally be located<br />
externally on the WTG foundation and the transition piece.<br />
6.9.2 The ancillary equipment would be defined as:<br />
� J-tubes;<br />
� Access and rest platforms;<br />
� Access ladders;<br />
� Boat access system; and<br />
� Corrosion Protection Systems.<br />
J-tubes<br />
6.9.3 J-Tubes comprise the metal tubes that protect the inter or intra-array<br />
electrical cables, as they travel up the foundation structure to the TP. The<br />
metal tubes at the bottom of the foundation structure would generally be<br />
curved to support the inter or intra-array cable as it transitions from a<br />
horizontal to a vertical position. Each J-tube would house one inter or intraarray<br />
cable, therefore, more then one J-tube would be required per<br />
foundation structure to facilitate the incoming and out going array cables.<br />
6.9.4 The J-tube can extend from the seabed all the way up the foundation<br />
structure to the TP. If the foundation structure is a monopile or space-frame<br />
type the J-tubes can be housed externally or internally to the structure. Jtubes<br />
located inside the foundation structures have an additional level of<br />
protection. External attachment of J-tubes would be more likely with GBS<br />
foundation structures.<br />
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Boat landing system access<br />
6.9.5 The design of boat landing facilities, access ladders and subsequent<br />
platforms would be driven by the type and largest size of boat anticipated to<br />
be used in the maintenance programme. It would be reasonable to assume<br />
that marine grade floodlights would be fitted to illuminate the boat landing as<br />
required during hours of darkness. Typically the lights would be controlled<br />
from the wind farm control room.<br />
Access ladders<br />
6.9.6 Experience on GGOWF has shown that two vertical access ladders would be<br />
required and it is anticipated that a similar system would be used on the<br />
GWF project where TP solutions would be adopted. The ladders would be<br />
approximately 600mm wide with rungs at 300mm vertical intervals. To<br />
protect the lower ladder a permanent fender system would be located either<br />
side, which also provides a safety zone for personnel. The fender system<br />
provides further guidance or a buffer system for the landing craft as it<br />
maintains its position in the water next to the TP to allow the transfer of<br />
personnel.<br />
6.9.7 To ensure the safety of personnel climbing up the ladder a fixed inertia reel<br />
safety system is used. Personnel would attach themselves to the fixed safety<br />
system which allows them to climb the ladder freely, however in the event of<br />
a fall or slip it locks preventing movement backwards.<br />
6.9.8 The initial ladder would typically be approximately 11m long and extends<br />
below the lowest astronomical tide (LAT) to ensure access at all tidal states.<br />
A rest platform would be located between the two ladders. The second<br />
ladder would typically be approximately 5m long and would also be fitted with<br />
a fixed inertia reel safety system but not the fixed fender system.<br />
6.9.9 If space frame structures are selected the upper ladder may be replaced by a<br />
stairway. This would also be the case if GBS foundations are selected<br />
without a TP.<br />
Access platform<br />
6.9.10 All structures whether TP’s, space frames, GBS would have to have access<br />
platforms of a minimum 1m width. The access platform would also include<br />
an integral laydown area adjacent to the access door.<br />
6.9.11 A small davit crane capable of lifting up to approximately 250kg, would be<br />
mounted on the main platform, beside the lay-down location. This would be<br />
used to lift the necessary equipment from the boat onto the platform, or vice<br />
versa. Additionally some WTG would have cameras located on the main<br />
platforms to allow remote observation to take place. These would allow an<br />
onshore based O&M team to assess the sea state and weather conditions at<br />
the WTG, whilst also maintaining visual contact with maintenance operations<br />
in the field.<br />
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6.9.12 During the WTG installation phase there is the potential that temporary<br />
generators would be positioned on the main platforms, as the process would<br />
require electricity which might not be available from the shore. If this<br />
situation arises then the correct environmental mitigation would be<br />
introduced, such as ensuring the generator would be effectively bunded.<br />
6.10 <strong>Wind</strong> Turbine Generators<br />
Concept summary<br />
6.10.1 The WTG consist of three primary components (see Plate 6.16):<br />
� The tower;<br />
� The nacelle; and<br />
� The rotor.<br />
Plate 6.16 WTG component overview<br />
Source: The Crown Estate (2010)<br />
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WTG tower<br />
6.10.2 The WTG tower is the component which gives the rotor the necessary height.<br />
The structure is likely to consist of up to four tapering steel tubular sections,<br />
which would be lifted into place and secured together by bolting. Each tower<br />
section would arrive on location with pre-installed internal fittings, thus aiding<br />
the secondary installation phase.<br />
6.10.3 The bottom tower section would be bolted via a flange to the TP. Similarly<br />
the top tower section would be flanged to facilitate the connection with the<br />
nacelle component.<br />
The nacelle<br />
6.10.4 The nacelle houses the electro-mechanical elements of the WTG, or more<br />
simply a machine that can turn rotational motion into electrical energy.<br />
Depending on the WTG supplier additional equipment such as the WTG<br />
transformer would also be housed on the nacelle.<br />
The rotor<br />
6.10.5 The rotor is the device which, through circular motion, extracts the energy<br />
from the wind. Increasing the blade length allows more energy to be<br />
extracted from the passing wind through a greater ‘swept area’. The blades<br />
can be feathered or twisted (i.e changing their pitch) to maintain a particular<br />
speed. Three-bladed rotors are the most common type and are envisaged<br />
for use on the GWF project.<br />
WTG manufacturing and transportation<br />
6.10.6 The primary components of the WTG are typically fabricated in smaller units<br />
for transportation purposes, for example the blades for the rotor are<br />
manufactured individually.<br />
6.10.7 The method of transportation to site would depend on WTG manufacturer’s<br />
recommendations, the type of installation vessel and the timing of installation.<br />
The GGOWF WTG components were transported to the offshore location<br />
then lifted into position, as opposed to pre-assembly onshore of the tower<br />
and nacelle, followed by shipment to site. Either method may be adopted by<br />
the GWF project.<br />
Fluids and oils<br />
6.10.8 The volume of fluids and oils required by a WTG is greatly dependent on the<br />
drive train and pitching technology of the specific WTG. If the oil in the<br />
nacelle (i.e. the gearbox and hydraulic tanks) were to leak under any<br />
circumstances then it would most likely leak down the walls of the tower, on<br />
the inside, and would accumulate under the access platform at the base of<br />
the transition piece.<br />
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6.10.9 During operation the fluids may be under high pressure, and mechanical<br />
failures could lead to high pressure fluid release. In such an event the<br />
machine would be shut down automatically due to low pressure/ low level<br />
alarms etc. A hydraulic failure in the hub would have a similar outcome.<br />
6.10.10 WTGs are designed to prevent any significant accidental leakages of such<br />
fluids and oils, as the bottom of the tower/ transition pieces are typically air<br />
tight with sufficient containment incorporated into the structure to prevent<br />
accidental fluid release. Furthermore, containment would also be included in<br />
the design and construction of the nacelle and the top tower platform. All of<br />
the main bearings including the slew, hub and pitch would also be equipped<br />
with grease catchers.<br />
WTG installation<br />
6.10.11 Installation methods of WTG vary and include assembly of the turbine tower,<br />
nacelle and rotors individually whilst at sea, through to transfer of complete<br />
turbines from land. Most typically the towers would be mounted vertically on<br />
a dedicated heavy lift installation vessel and one or more blades joined to the<br />
rotor hub before shipment, with the final blade/s installed once the tower and<br />
rotor are in place.<br />
WTG operational noise<br />
6.10.12 When a windfarm is operational the main source of underwater noise is<br />
mechanically generated vibration from the turbines transmitted into the sea<br />
through the structure of the support pile and foundations (Nedwell et al.<br />
2003). Subacoustech (Nedwell et al., 2007) have undertaken a review of<br />
four operational wind farms (North Hoyle, Scroby Sands, Kentish Flats and<br />
Barrow). The available data indicated that the noise generated by a working<br />
turbine is significantly lower than the noise created during construction by<br />
piling. However, while construction noise may only span a period of a few<br />
months, operational noise would span the lifetime of the windfarm (Nedwell<br />
et al., 2007).<br />
6.10.13 The study findings revealed that the level of noise from operational<br />
windfarms was very low and was not considered to pose any risk to fish and<br />
marine mammals (Nedwell et al., 2007). In some instances, operational<br />
noise could be recognised by the tonal components caused by rotating<br />
machinery and by its decay with distance. However, the noise generated by<br />
the operating WTG, even in the immediate vicinity, only dominated over the<br />
background noise in a few limited bands of frequency and equated to a rise<br />
of only a few dB above background noise levels. In some cases, the tonal<br />
noise caused by the WTG was dominated by the tonal noise from distant<br />
shipping (Nedwell et al., 2007).<br />
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WTG options<br />
6.10.14 There are several WTG models of varying rotor diameters which are being<br />
considered. The wind farm would consist of up to a maximum of 140 WTGs,<br />
with an output not exceeding 504MW, and a rotor diameter range of 107m to<br />
164m. These rotor diameters represent WTGs in the order of 3.6MW to<br />
7MW capacity based on currently available models. All options would have a<br />
minimum clearance distance of 22m above mean high water springs<br />
(MHWS).<br />
6.10.15 WTGs normally operate within a predetermined range of wind speeds,<br />
typically starting at 3.5ms -1 and producing their maximum power at<br />
approximately 12ms -1 . WTGs typically shut down at wind speeds greater<br />
than 25ms -1 , in order to avoid damage.<br />
6.10.16 For the assessment of the worst realistic case, three turbine examples were<br />
chosen to represent the greatest levels in a number of different parameters,<br />
such as hub height, tip height and maximum number. Details of the<br />
dimension and key criteria of the maximum and minimum size ranges<br />
considered for the GWF assessment are provided in Table 6.4. These are<br />
not intended to be exhaustive of all the turbine examples that may be utilised,<br />
however they provide a sound basis for identifying the realistic worst case<br />
based on upper and lower size limits in each of the areas of environmental<br />
assessment.<br />
Table 6.4 Summary of the WTG parameters<br />
WTG detail 107m rotor 120m rotor 164m rotor<br />
Typical MW rating (for<br />
easy referencing)<br />
Minimum clearance above<br />
MHWS<br />
Maximum No. WTG in<br />
array<br />
3 - 3.6MW 3.6 - 4MW 6 - 7MW<br />
22m 22m 22m<br />
140 140 72<br />
Hub height (LAT) 79.5m 86m 120m<br />
Maximum tip height 135m 146m 195m<br />
Rotor diameter 107m 120m 164m<br />
Cut in/out speed<br />
Maximum rotor speed 13rpm<br />
Maximum tip velocity 73ms -1<br />
3-5ms -1 cut in,<br />
25ms -1 cut out<br />
3-5ms -1 cut in,<br />
25ms -1 cut out<br />
3-5ms -1 cut in,<br />
25ms -1 cut out<br />
13rpm 11.5rpm<br />
81.7ms -1 90.3ms -1<br />
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WTG detail 107m rotor 120m rotor 164m rotor<br />
Total project swept rotor<br />
area<br />
Minimum grid downwind<br />
(8D)<br />
Minimum grid crosswind<br />
(6D)<br />
1.264km 2<br />
1.6km 2<br />
1.3km 2<br />
856m 960m 1,212m<br />
642m 720m 984m<br />
6.10.17 The final decision on the WTG type taken forward by GWF would depend on<br />
the WTG available in the market place at the time of procurement, the<br />
economics associated with the manufacture, transportation and installation of<br />
the available options, and the outcome of detailed FEED and optimisation<br />
studies post consent.<br />
6.10.18 Table 6.5 provides a summary of the possible WTG build-out scenarios.<br />
Table 6.5 Example WTG build-out scenarios<br />
Build-out scenarios – WTGs<br />
One size class only<br />
One size class only<br />
Two size classes, different phases<br />
Optimised smaller project with smaller 3 –<br />
3.6MW or 3.6 - 4MW WTG on monopiles in<br />
shallow water<br />
<strong>Project</strong> utilising larger WTG class machine<br />
(e.g. 6 – 7MW) on either space-frame or<br />
suitable foundation for all water depths<br />
First stage of development with 3-3.6MW or<br />
3.6-4MW on monopile foundations, second<br />
stage utilising larger turbines, e.g. 6-7MW<br />
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6.11 Ancillary Infrastructure<br />
Offshore substation platform(s)<br />
6.11.1 The principal purpose of the Offshore Substation Platform (OSP) is to house<br />
the transformers required to increase the distribution voltage (typically 66kV<br />
or above) of the inter and intra-array cables to a higher export voltage<br />
(132kV) for the export cables.<br />
6.11.2 It is envisaged that between one and three OSPs would be required for the<br />
GWF project. The flexibility in the number considered is reflective of the<br />
potential to develop a range of layouts utilising one, two or three of the three<br />
distinct Development Areas.<br />
Topsides<br />
6.11.3 The topside is the name for the structure which would be placed on top of the<br />
foundation structure and completes the OSP. It may be configured in either a<br />
single or multiple deck arrangement. Decks would either be open with<br />
modular equipment housing or the structure may be fully clad. All weather<br />
sensitive equipment would be placed in environmentally controlled areas.<br />
6.11.4 The offshore substation(s) would be up to 75m in height (30m from LAT to<br />
topside and then 45m for height of substation unit).<br />
6.11.5 The OSP would be fabricated at a quayside facility to enable the transfer of<br />
the topside structure onto a barge for transportation offshore. Whilst at the<br />
quayside the topside would be fitted out internally with all the necessary<br />
equipment. As far as possible the equipment would be made ready for<br />
operation prior to being moved offshore. Environmental mitigation measures,<br />
such as transformer bunding, would be fully operational prior to the OSP<br />
transportation phase.<br />
6.11.6 The OSP would typically accommodate the following:<br />
� Helicopter landing facilities;<br />
� Refuelling facilities;<br />
� Potable water;<br />
� Black water separation;<br />
� Medium (MV) to high voltage (HV) power transformers;<br />
� MV and/or HV switch gear;<br />
� Instrumentation, metering equipment and control systems;<br />
� Standby generator;<br />
� Auxiliary and uninterruptible power supply systems;<br />
� Marking and lighting;<br />
� Emergency shelter, including mess facilities;<br />
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� Craneage; and<br />
� Control hub.<br />
Discharges<br />
6.11.7 The OSP’s drainage system would collect the waste water as well as<br />
connecting the bunded areas. The drainage system would incorporate a<br />
separation unit which would separate any contamination from the collected<br />
water. The collected water would be re-circulated through the separator until<br />
the water complies with the Environmental Agency’s requirements, prior to<br />
discharging to the sea.<br />
6.11.8 The collected contamination would be discharged into a storage facility, for<br />
transporting to shore and the appropriate disposal.<br />
Foundations<br />
6.11.9 The offshore platform(s) foundation would most likely comprise a spaceframe<br />
foundation system analogous to that described in Section 6.7 for WTG<br />
space-frame foundations, only larger in dimensions (Table 6.1). However,<br />
at this stage GWFL may consider all foundation types as detailed for the<br />
WTGs in Table 6.1.<br />
6.11.10 The existing GGOWF project uses a square lattice type foundation with<br />
cylindrical piles, driven through sleeves at each of the four space frame legs<br />
into the seabed to secure in place. The advantages of the lattice space<br />
frame are that it provides the most protective solution for the incoming inter<br />
and intra-array and export submarine cables and also enables the OSP to be<br />
deployed in any of the water depths within the array. Details of the maximum<br />
space frame dimensions are provided in Table 6.1.<br />
6.11.11 As an example, the lattice space frame would be fabricated onshore and<br />
subsequently loaded onto a transportation barge that would deliver it to the<br />
required location, before being placed onto the seabed by an HLV or jack-up<br />
barge. The pilling options would be the same as a space-frame to support a<br />
WTG (i.e. pre or post installed cylindrical piles or suction piles (Section 6.7)).<br />
6.11.12 Corrosion measures for the space frame would be a mixture of pre-coating<br />
and either sacrificial anodes or an impressed CP system, again following the<br />
oil and gas industry guidelines and certification channels. The CPS methods<br />
for the space frame would be the same as those discussed in the previous<br />
Section 6.7.<br />
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Accommodation platform<br />
6.11.13 An accommodation platform may be required to provide accommodation and<br />
suitable landing points (for vessels and or helicopter) for any onsite<br />
coordination of emergency marine activities.<br />
6.11.14 The foundation for an accommodation platform would be similar to the OSP<br />
(namely space-frame), but smaller in dimension. The topside would be large<br />
enough to contain emergency shelter and facilities for crews undertaking the<br />
necessary work offshore. Power and communication links would need to be<br />
installed, with a standby generator in case mains electrical supply was lost.<br />
Fabrication of the space frame and topside would take place onshore, with<br />
transportation to the offshore location before being lifted into position.<br />
Collection station<br />
6.11.15 Once the location of the turbines has been finalised, then the design to link<br />
the turbines together can be undertaken. The electrical design study would<br />
determine if a collection station is needed. Subsequent development of the<br />
initial design <strong>proposal</strong> would then determine the location, substructure and<br />
dimensions of the necessary collection station.<br />
6.11.16 The role of the collection station would be to facilitate the electrical<br />
connection of several turbine electrical strings so that the total generated<br />
power from them can be exported on a single cable.<br />
6.11.17 The collection station would be housed on a similar substructure to that of the<br />
WTG. The foundation type for the collection stations would either be a<br />
monopile or a space-frame type structure. Either of these structures would<br />
contain a number of J-tubes<br />
6.11.18 Transformers, if required, would be located on the collection stations to step<br />
up the voltage, for instance from 33kV to 66kV. This would assist the energy<br />
efficiency of the site as higher transmission voltages incur less electrical<br />
power loss. This must be offset with the fact that transformers themselves<br />
consume electrical energy. Consequently the installation of transformers<br />
would be a less attractive option.<br />
6.11.19 The topside of the collection station would comprise electrical switchgear,<br />
thus dimensionally small and lighter than a complete WTG. If the collection<br />
station was required to house a transformer the floor plate would be larger.<br />
Meteorological mast(s)<br />
6.11.20 Up to three permanent meteorological (met) masts are envisaged for the<br />
GWF project. The met masts would be installed in key locations within the<br />
GWF licensed area. Information detailing the wind direction and strength<br />
would be recorded continuously via the SCADA system, with the information<br />
retrieved bi- monthly via a visit to the offshore location.<br />
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6.11.21 The met masts are used to verify the wind turbine’s MW output, and<br />
additionally feed the real time data into the wind forecasting module to help<br />
predict the next day’s wind pattern. The met mast would be placed on a<br />
foundation structure of similar type to those described in the previous section<br />
i.e. monopile, space frame, gravity base or suction bucket, which would be<br />
appropriate to the location of the installation. A topside, or deck protected<br />
from the elements, which is large enough to house electrical switch gear and<br />
communication equipment, along with back-up systems would be required.<br />
Ancillary structure summary<br />
6.11.22 Table 6.6 provides a summary of the offshore ancillary infrastructure.<br />
Table 6.6 Summary of the ancillary infrastructure<br />
Detail<br />
OSP / Collection station /<br />
Accommodation platform<br />
Maximum No. of infrastructure 4 3<br />
Maximum infrastructure<br />
height<br />
Foundation options<br />
6.12 Inter, Intra-array and Export Cables<br />
Met-mast<br />
75m 120m<br />
Monopile, GBS, spaceframe<br />
and suction-bucket<br />
(as detailed in Table 6.1)<br />
Monopile, GBS, spaceframe<br />
and suction-bucket<br />
(as detailed in Table 6.1)<br />
Inter and Intra-array cables<br />
6.12.1 Inter-array cables would be laid between the different areas and intra-array<br />
cables would be laid between turbines as shown in Figures 6.1 to 6.3.<br />
6.12.2 The inter and intra-array cables collect and transfer power generated in WTG<br />
to the OSP(s), potentially in different key areas of the project. The cables<br />
connect the WTG together into strings, with the maximum number of WTG<br />
connected together depending on WTG size and cable rating. The strings of<br />
turbines would then in turn be connected to the offshore platform, possibly<br />
via a collection station.<br />
6.12.3 The intra-array cables between adjacent WTG would be relatively short in<br />
length, typically in the range of 600m to 2,000m. However, some cables (e.g.<br />
those between the last turbine in the string and the OSP) could be<br />
significantly longer and may pass between arrays, i.e. becoming inter-array.<br />
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6.12.4 The precise inter and intra-array cable layout would be defined following<br />
detailed FEED studies. In addition, the decision as to whether a radial,<br />
looped or branched arrangement is adopted would be made following further<br />
site investigations and would be influenced by a combination of ground<br />
condition and economic factors (as for the WTG layout determination). For<br />
the purposes of the PER, indicative inter and intra-array cable layouts are<br />
provided in Figures 6.1 to 6.3.<br />
6.12.5 The cable size would be expected to increase from the far end of the strings<br />
to the OSP to accommodate the increasing power that would be carried. It is<br />
possible that up to five different cable sizes would be used throughout the<br />
wind farm.<br />
6.12.6 The inter and intra-array cables would typically be rated at 33kV, and would<br />
carry the electrical energy generated by the WTG to a central location. The<br />
inter or intra-array cable would be a single armoured submarine cable,<br />
containing 3 electrical conducting cores and an optical fibre cable. Plate<br />
6.17 shows the typical make-up of a single armoured submarine cable.<br />
Plate 6.17 Typical single armoured submarine cable<br />
Source: GGOWL, (2009)<br />
Export cables<br />
6.12.1 Export cables would be three phase Alternating Current (AC) cables with a<br />
rating of 132kV. The cable would be extruded cross linked polyethylene<br />
(XLPE) insulated and wire armoured for erosion protection.<br />
6.12.2 Up to four export cables would be required to transfer the wind farm output to<br />
shore. The final number of export cable circuits would depend on the final<br />
wind farm design. It is possible that the export cables will also allow for data<br />
to be transferred using spare optical fibres.<br />
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6.12.3 The export cables comprise the cabling from landfall to the wind farm site<br />
and any inter-connecting cabling between OSP within the potential separate<br />
array Areas (see Figures 6.1 to 6.3)<br />
Proposed export cable route<br />
6.12.4 A dedicated geophysical survey has been undertaken on a corridor between<br />
500m and 1,000m wide within which the export cable route would be<br />
established (see Chapter 10). A corridor of this width would be required to<br />
account for spacing between the four cables and any amendment of the<br />
cable route due to the navigation around obstacles including aggregate<br />
extraction (see Chapter 19 Human Activity), marine archaeology / wrecks<br />
and other magnetic and sonar contacts (see Chapter 20 Archaeology) and<br />
sandwaves (Chapter 10 Physical Processes):<br />
6.12.5 The philosophy behind this route selection is provided in Chapter 7 Site<br />
Selection and Alternatives. It should be noted that the export cable<br />
corridor, which has been agreed with The Crown Estate, reaches shore to<br />
the north of Sizewell; however the actual landfall will be to the south of<br />
Sizewell.<br />
6.12.6 The precise export route within this corridor would be established following<br />
detailed FEED studies and further site investigation post consent.<br />
Cable manufacture & transportation<br />
6.12.7 The estimated length of each export cable, depending on the final route,<br />
would be approximately 50km. This is established from the nearest offshore<br />
substation to the landfall at Sizewell. Additional export cables, up to two<br />
circuits (20km each), would be expected to connect the first OSP to the most<br />
distant OSP. Therefore, it is estimated that the total length of subsea export<br />
cable required would be up to 240km. Table 6.7 indicates the detail of<br />
typical AC export cables.<br />
6.12.8 Plate 6.18, below shows an AC export cable being loaded into a carousel - a<br />
circular rotating cage mounted onto the back of an installation vessel. The<br />
vessel transports the export cable to the required location from where it is<br />
pulled initially into position and then installed slowly into the seabed as<br />
described in the following sections.<br />
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Plate 6.18 Export cable being loaded into a carousel<br />
Cable installation<br />
Pre-installation works<br />
6.12.9 The preferred cable route would be surveyed (via the pre-construction<br />
geophysical survey) to locate any obstacles that may obstruct cable laying<br />
(e.g. rocks, wrecks, metal objects, unexploded ordnance). If an obstruction is<br />
located it would be assessed and an appropriate strategy would be<br />
established to remove or avoid the obstruction. Typically a Pre Lay Grapnel<br />
Run (PLGR) and ROV survey would be conducted to clear the obstruction.<br />
Where the obstacle is suspected to be UXO specialist mitigation would be<br />
employed to either avoid or make safe the obstruction.<br />
6.12.10 The geophysical surveys would also serve to identify the location of sand<br />
waves along the cable route so that an assessment can be made as to<br />
whether such features can be avoided or, if not, what level of seabed<br />
preparation (pre-lay sweeping) is required to ensure an appropriate burial<br />
depth is achieved in stable (i.e. non mobile) seabed conditions.<br />
6.12.11 Prior to cable installation, cable burial trials may be conducted in advance of<br />
the main installation programme to ensure that the chosen equipment would<br />
be suitable for the ground conditions encountered and that an appropriate<br />
burial depth can be achieved. If undertaken, any such trial may involve trials<br />
of lengths of up to 1km in each of the soil types likely to be encountered<br />
along the export cable route.<br />
Cable installation methods<br />
6.12.12 There are several different methods available for the installation of submarine<br />
cables:<br />
� Simultaneous lay and burial using a cable plough<br />
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� Post lay and burial using a jetting ROV<br />
� Simultaneous lay and burial/post lay and burial with a mechanical<br />
trencher.<br />
6.12.13 The final decision on installation method would be made on completion of the<br />
pre-construction geotechnical site investigation surveys. However, it is<br />
noteworthy that the GGOWF project has utilised a combination of ploughing,<br />
jetting and trenching to accommodate for the variation in sedimentary<br />
conditions along the cable routes.<br />
Cable burial by ploughing<br />
6.12.14 Cable burial ploughs cut through the seabed, lifting the soil from the trench.<br />
Cable ploughs are designed to cut a narrow trench, with a slot of material<br />
temporarily supported before falling back over the trenched cable.<br />
6.12.15 The advantage of this method is that burial can be achieved as the cable is<br />
laid, thus minimising risk to the cable. However, the number of vessels which<br />
can carry out this method and that have the required cable carrying capacity<br />
for “heavy” power cable is limited.<br />
6.12.16 The performance of a plough and the depth of burial which can be achieved<br />
are a function of plough geometry and seabed conditions, with dense / stiff<br />
soils providing the greatest challenge.<br />
6.12.17 A typical cable burial plough (such as the Sea Stallion 4, as shown in Plate<br />
6.19) excavates to a width sufficient to enable insertion of a cable up to<br />
280mm in diameter. The plough itself would typically be around 5m in width,<br />
although the operating footprint on the seabed would be much smaller than<br />
this.<br />
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Plate 6.19 Example cable burial plough<br />
Source: www.VSMC.nl<br />
Cable burial by jetting<br />
6.12.18 Where seabed conditions are predominantly soft sediment material it may be<br />
considered appropriate to bury the array cables with a Directionally<br />
Positioned (DP) vessel post installation.<br />
6.12.19 Under this process the cable would be laid on the seabed first and an ROV<br />
(Remote Operated Vehicle) fitted with high-pressure water jets is<br />
subsequently positioned above the cable. The jets fluidise a narrow trench<br />
into which the cable sinks under its own weight. The jetted sediments settle<br />
back into the trench and with typical tidal conditions the trench coverage<br />
would be reinstated over several tidal cycles.<br />
Cable burial by trenching<br />
6.12.20 In locations where seabed conditions comprise very stiff soils (typically over<br />
100kPa) and/or bedrock, ploughing and jetting techniques may not be<br />
appropriate for cable burial.<br />
6.12.21 One approach for installing cables in very stiff/hard seabeds would be to use<br />
mechanical trenchers which can either be used to simultaneously bury the<br />
cable as it is laid or in a “post lay” mode where the cable is laid by one vessel<br />
and burial is achieved by another vessel spread following on behind.<br />
Simultaneous lay and burial of the cable tends to be preferred since this<br />
reduces risk to the cable from exposure. However, if a post lay burial<br />
solution is used then typically the length of time of exposure would only be a<br />
few hours (depending on the exact arrangements). During this time any<br />
unburied lengths of cable would be protected using a guard vessel.<br />
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6.12.22 It should be noted that simultaneous lay and burial can also be achieved by<br />
ploughing in stiff materials to 140KPa and above (eg chalk) by use of<br />
specially designed “rock ripping” ploughs as well as certain types of<br />
“standard” subsea plough. For example, in the recent installation on<br />
GGOWF the export cable was installed through stiff/hard crag material using<br />
a standard “Sea Stallion” subsea plough. Trench spoil would be left to<br />
naturally backfill, which typically takes two or three tides<br />
Plate 6.20 Example cable burial trencher<br />
Source: Pharos offshore group<br />
Cable installation procedure<br />
6.12.23 A cable barge or specialist cable installation vessel is likely to be required to<br />
install the cable into the seabed. The array cables would be supplied on<br />
cable reels or loaded onto the vessel in one continuous length. Collection<br />
would take place from the manufacturer’s facilities or holding docks prior to<br />
transportation to the ploughing vessel.<br />
6.12.24 The vessel then travels to site and takes up position adjacent to the start<br />
location (WTG for inter and intra-array cabling or OSP / the shore for export<br />
cabling). The vessel would either hold station via a DP system or set<br />
anchors in a stationary mooring pattern. One end of the array cable would<br />
then be floated from the cable reel towards the substructure / shore. The<br />
cable would then be laid away from the substructure / shore in a direction<br />
towards the landfall / OSP. The cable installation vessel would either move<br />
under DP control or by hauling on its anchors; if the secondary method is<br />
used then redeploying the anchors would be required.<br />
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6.12.25 Depending on the design of the relevant substructure, the cable is either<br />
sunk and fed through the J-tube and lifted / pulled into the transitional piece<br />
or pulled through a pre-installed J-tube attached externally to the<br />
substructure.<br />
6.12.26 The cable installation vessel’s ability to get close to shore is dependent on<br />
vessel draft, (but is typically around 10m) at which point water depths are too<br />
shallow to proceed. At this time the installation vessel would hold its position<br />
either by use of Differential Global Positioning System (DGPS) or anchors<br />
whilst the cable is brought (floated) to shore. If a cable barge is used then<br />
their draft is suitably shallow to enable access to shore. The process of<br />
connection to shore is discussed in detail in Section 6.13.<br />
Cable burial depths<br />
6.12.27 Appropriate cable burial depth would be determined by a detailed hazard<br />
identification survey, which would assess the different locations and the<br />
various shipping and dredging activities. It is possible that the hazard<br />
identification survey would identify places where the depth may vary due to<br />
local features, such as:<br />
� Sand waves<br />
� Erosion of the seabed<br />
� Intense demersal fishing<br />
� Existing infrastructure (such as cables) or observed seabed obstacles.<br />
6.12.28 Export, inter and intra-array cable target burial depth could be up to 1.5m.<br />
Typically though the burial success may be closer to 1m, although this would<br />
be highly dependent upon equipment used and ground conditions, and with a<br />
minimum aim of achieving 0.6m.<br />
Cable lay protection<br />
6.12.29 Achieving target burial depths for export, inter and intra-array cables would<br />
not be possible in close proximity to the WTG and OSP, where the cables<br />
rise up to connect to the J-tube of these structures. Typically these sections<br />
may be in the region of 20m in length (DOWL, 2009).<br />
6.12.30 There are three surface based protection measures which may be utilised for<br />
cable protection:<br />
� Extension of the scour protection rock dumping (if being used) to<br />
cover the final 20m of cable on the seabed<br />
� Use of concrete mattresses which are lifted and placed over the cable<br />
sections (see cable crossings section for further detail of this<br />
methodology). This methodology is sometimes supplemented with the<br />
use of sandbags to stabilise the edges of the mattresses<br />
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� Use of grout bags which can be placed over the lengths of cable and<br />
then inflated with structural grout. The grout then cures to provide an<br />
effective cover protection system for the cables. This approach<br />
requires diver assistance.<br />
6.12.31 Alternative protection may also be required where it is impossible to achieve<br />
the target burial depth (e.g. where seabed conditions prevent access for the<br />
installation equipment). Experience from the adjacent GGOWF project would<br />
suggest that the likelihood for significant levels of cable lay protection under<br />
such circumstances would be limited.<br />
Cable separation<br />
6.12.32 Cables must be laid with a separation distance so that, in the event of a fault,<br />
repairs can be carried out without risk of damaging the adjacent cables.<br />
6.12.33 It is anticipated that a nominal spacing of 60m between cables would be<br />
utilised, which would be sufficient to avoid conflict with anchor spread, whilst<br />
decreasing the risk from damage through cable ploughing activity for<br />
adjacent cables. The cable separation would need to be reduced to a<br />
suitable width at the shoreline as the cables approach the HDD ducts at the<br />
landfall point, however this approach is subject to detailed design. Therefore<br />
whilst the export corridor is shown in Figure 1.1 (Chapter 1) approaching the<br />
shore at a consistent offset from the existing GGWOF export cables, the<br />
separation would reduce signficantly on the approach to shore to allow the<br />
cables to pass south of Sizewell, as shown in Figure 1.2 (Chapter 1). This<br />
would result in the GWF cables being in the GGOWF export cable corridor as<br />
the GWF cables approached the shore. Cable separation for the crossing of<br />
telecommunication cables would be subject to final agreement with the third<br />
party owners.<br />
Cable crossings<br />
6.12.34 There are four telecommunication cables that would require crossing (three<br />
by the export cable route and one within Areas A and B (see Chapter 19).<br />
Given that there would be up to four export cables, there would be up to 12<br />
crossings required on the export route. The number of crossings associated<br />
with the intra-array cabling would be determined following design<br />
optimisation and confirmation of final layout post consent.<br />
6.12.35 The International Cable Protection Committee (ICPC) has issued a<br />
recommendation for crossings arrangements between telecommunication<br />
cables and power cables. This recommendation outlines how, and why, a<br />
Crossing Agreement should be put together, but does not describe the<br />
physical construction of a crossing.<br />
6.12.36 There is no single universally accepted crossing design that would be<br />
applicable in all situations. Designs would vary with the seabed properties at<br />
the particular location. Each crossing would have a range of features<br />
possibly unique to that location, based on:<br />
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� The physical properties of the crossing product, for example the cable<br />
size and weight, bend radius and armouring<br />
� Protection requirements relative to the hazard profile, including depth<br />
of burial or extent of mattress/rock cover<br />
� The physical properties and protection status of the crossed product<br />
� Seabed properties at the crossing point, for example substrate type,<br />
morphology and stability - presence of mobile bedforms<br />
� Any constraints placed by the crossed party, for instance location and<br />
burial determination standards, maintenance clearance zone, plough<br />
approach limits and notification zone.<br />
6.12.37 The minimum vertical separation distance between the two cables would<br />
likely be governed by the requirements of the crossed party and construction<br />
methodology. This is normally 0.3m (from a mechanical separation point of<br />
view). Assuming that the crossed cables are buried by 1.5m and a 0.3m<br />
mattress is placed underneath the GWF cables, a minimum separation of<br />
1.8m would be likely.<br />
6.12.38 The components most commonly used to protect telecommunication cables<br />
would be flexible mattresses and graded rock. These components may be<br />
used exclusively or in combination.<br />
6.12.39 The telecommunication cables on the export cable route would require<br />
multiple crossings (given that there would be four export cables). Crossing<br />
the cables at one point, via a single physical structure, has benefits through<br />
reducing installation time and expense.<br />
Mattresses<br />
6.12.40 Mattresses made from elements of concrete or bitumen are widely used to<br />
protect from seabed hazards where burial is not viable or is not effective.<br />
The most common form of mattress is that made of concrete elements<br />
formed on a mesh of polypropylene rope, which would conform to changes in<br />
seabed morphology. Bevelled elements are used on the periphery to create<br />
a lower profile to encourage hazards such as trawl gear to roll over the<br />
mattress. Typically, mattresses of 6m by 3m and 150mm to 300mm in<br />
thickness would be used for cable crossings.<br />
6.12.41 If the sediment dynamics are appropriate, mattresses fitted with<br />
polypropylene ‘fronds’ may be used to enhance the protection provided, as<br />
the fronds encourage transient sediments in the water column to be<br />
deposited, in the best case creating a protective sand bank. Where the burial<br />
depth of a cable is zero, shallow or ambiguous mattresses can be configured<br />
to reduce the risk of direct contact. Plate 6.21 shows various designs that<br />
have been proposed historically.<br />
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Plate 6.21 Fully mattressed crossing designs<br />
Source: GGOWL, 2009<br />
6.12.42 A site specific geophysical survey would confirm the precise crossing point<br />
(with areas of level seabed and suitable cover over the existing cable being<br />
preferable). Mattresses are then lowered into place from a dedicated vessel,<br />
with divers to ensure accurate deployment. The export cable(s) would be<br />
laid on the primary layer of mattresses and a second layer of protective<br />
mattresses would subsequently be installed on top of the cable. The cable<br />
burial equipment would then bury the cable into the sediment, and extra<br />
mattressing or rock dump material applied to ensure suitable burial depth<br />
would be maintained where the cable re-enters the sediment.<br />
Rock placement<br />
6.12.43 Rock placement has long been established as a method for constructing<br />
crossings. The rock used would normally be imported from land quarries,<br />
although sea aggregates can also be used, the grain sizes being tailored to<br />
achieve the necessary protection. Rock would usually be deposited by a fall<br />
pipe vessel where the water depth is adequate as this would be the most<br />
efficient method of getting the material onto the seabed. In very shallow<br />
waters a specialist vessel fitted out with basic equipment for pouring the<br />
aggregate over the side may be used.<br />
6.12.44 On fall pipe vessels, the aggregate would be conveyed to the side of the ship<br />
and freefalls down a chain-mail pipe. At the end of pipe would be an ROV,<br />
which may be used to adjust the delivery point relative to the ship. The<br />
combined movements of the ship and ROV would be used to construct the<br />
necessary bridging and protection berms. The fallpipe ROV would be used<br />
to survey the position and shape of structures created, using acoustic<br />
profilers and other devices.<br />
6.12.45 Rock dumping is a relatively quick operation and is not as weather<br />
dependent as mattressing.<br />
Cables summary<br />
6.12.46 Table 6.7 provides a summary of the offshore cabling system.<br />
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Table 6.7 Summary of the cable parameters<br />
Cable detail Inter and intra-array cables Export cables<br />
Maximum voltage 66kV 132kV<br />
Maximum external cable<br />
diameter<br />
213mm 258mm<br />
No. cables TBC 4<br />
Total length Up to 200km 60km * 4 (cables)<br />
Target burial depth Circa 1.5m Circa 1.5m<br />
Burial method<br />
No. of cable crossings<br />
Cable protection area<br />
Plough / jetting Plough / jetting /<br />
Trenching<br />
TBC following design<br />
optimisation<br />
TBC following design<br />
optimisation<br />
6.13 Cable Landfall and HDD Works<br />
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12<br />
5,400m 2<br />
6.13.1 Export cables would be laid from a specialist vessel, most likely to be an<br />
anchored barge, due to the shallow nature of the shore approaches. The<br />
barge would require two attendant anchor handlers for positioning and a tug<br />
for transiting.<br />
6.13.2 The programme for each export cable lay is expected to be 25-30 days<br />
including a weather allowance. A few days before the vessel arrives,<br />
preparations would be made on the beach. This would include the creation<br />
of up to four HDD ducts (to enable the export cables to be brought through to<br />
the onshore transition pits) inland of the sea defences (see Plate 6.22). This<br />
would be to the north of the existing GGOWF works, as depicted in the<br />
footprint shown on Figure 1.2 in Chapter 1. The working area associated<br />
with these sites would be approximately 25m by 25m. The trench from the<br />
duct would be extended down to low water in order to bury the cables (see<br />
Plate 6.23).<br />
6.13.3 The end of the relevant HDD duct would be excavated during the low water<br />
period. The duct drawstring would be connected to a winch wire on its<br />
landward side and the wire then pulled in a seaward direction and connected<br />
to the cable end on board the lay vessel. The cable would then be pulled<br />
ashore by a land based winch behind the onshore transition pit. If a subsea<br />
plough is being used to bury the cable offshore, it would be pulled ashore at<br />
the same time and the cable loaded into it before it is pulled through the duct<br />
and into the onshore transition pit. It is anticipated that this process would
take at most two days to complete, from the arrival of the vessel carrying the<br />
export cable.<br />
6.13.4 Once pulled through the HDD duct the export cable would be buried in the<br />
intertidal and nearshore approaches (Plate 6.23). The void between cable<br />
and the duct wall would most likely be filled with bentonite to aid dissipation<br />
of heat away from the cable.<br />
Plate 6.22 Example HDD duct<br />
Plate 6.23 Example trench to enable intertidal cable burial at GGOWF<br />
Source: GGOWL<br />
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6.13.5 The HDD works to create the connection between the onshore transition pit<br />
and the HDD ducts on the beach would involve drilling an arc between the<br />
two points, to pass underneath a feature to be avoided (namely the sensitive<br />
foreshore habitats), and exits at a predetermined completion point. Plate<br />
6.24 provides a simplified typical HDD arrangement.<br />
Plate 6.24 Typical (simplified) HDD arrangement<br />
Rig Site Pipe Site<br />
Source: Balfour Beatty Power Networks Limited<br />
6.13.6 HDD requires a working area at each side of the proposed drill. One working<br />
area would be required for the rig site and another for the pipe site. The pipe<br />
site would effectively be the cable landfall location, and the rig site would be<br />
the exit location (approximately the location of the onshore transition pit).<br />
6.13.7 The rig and ancillary equipment would be set up on a level, firm area<br />
approximately 20m by 15m in size. At the pipe site an area approximately<br />
20m by 20m would be required. There would need to be sufficient room in a<br />
direct line behind the drill exit point to accommodate the complete length of<br />
the fabricated product pipe string. Both the rig site and pipe site would<br />
require entry (or launch) and receiving pits. These would need to be<br />
approximately 2.5m by 1m and 1m deep. Following completion of the HDD<br />
exercise excavated materials would be replaced into the pits, where excess<br />
waste material is generated this would be re-used or disposed of in<br />
accordance with the site waste management plan.<br />
6.13.8 The rig site and the pipe site would be securely fenced to ensure a safe site,<br />
with safe access and egress for site staff, any visitors required and the<br />
emergency services.<br />
6.13.9 A non-saline water supply at the rig site would be necessary within 100m of<br />
the drilling rig to facilitate the installation of drilling mud (bentonite, which acts<br />
as a lubricant during the process). If there is no suitable water supply on site<br />
this can be provided by tanker.<br />
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6.13.10 A mud lagoon would be required to capture and recycle drilling mud during<br />
the drilling process and to ensure it does not exit the site. The plan area of<br />
the lagoons may vary but would be a maximum of 5m by 5m. The depth of<br />
the lagoons would generally be 0.8m but this may vary according to local<br />
topography. In any event excavations would be plastic lined and protected<br />
with ‘Heras’ type fencing. Mud waste from this activity would be disposed of<br />
in accordance with the site waste management plan.<br />
6.13.11 The first stage of the drill involves a small pilot hole being drilled with a<br />
cutting / steering head to set the path of the arc from the rig site towards the<br />
pipe site. When the pilot bore is completed, the cutting / steering head would<br />
be replaced with an appropriately sized back-reamer at the pipe site and<br />
pulled through the pilot hole from the drill rig towards the rig site to enlarge<br />
the diameter of the hole. Depending on the final borehole diameter required,<br />
it may be necessary to carry out the back-reaming in several stages, each<br />
time increasing the borehole diameter gradually. Once the required diameter<br />
has been drilled, the back-reamer would be sent through the bore one or two<br />
more times to ensure that the hole is clear of any large objects and that the<br />
mud slurry in the hole is well mixed.<br />
6.13.12 On the final pass, the product pipe (the cable ducts in this case) would be<br />
connected onto the back-reamer and the drill string at the pipe site, using an<br />
extending sealed towing head. The drill string would then be pulled from the<br />
drill rig and retracted to the rig site cutting a larger diameter (clearance) bore<br />
whilst also installing the new pipe (the cable ducts).<br />
6.13.13 The drill process would be repeated until all required boreholes are drilled<br />
and all of the cable ducts are installed. The HDD exercise would typically<br />
require one week to drill each hole, and each drill string can be pulled<br />
through in a single day.<br />
6.13.14 To avoid damage to the sensitive foreshore habitats during the HDD<br />
exercise, a temporary road surface (gridded matting or similar) would be<br />
used for any beach access to avoid damage from heavy plant and other<br />
construction vehicles. It is anticipated that the temporary access route would<br />
follow a similar alignment to that used during the beach works undertaken by<br />
GGOWL. In addition, when the entry pit is excavated on the beach, the<br />
excavated shingle would be segregated and stored to ensure that the shingle<br />
layers are returned in the same orientation to minimise impact upon the<br />
integrity of the structure of the shingle.<br />
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6.13.15 A temporary beach compound would be required at the landfall location to<br />
accommodate beach anchors and for the temporary storage of plant and<br />
machinery during landfall operations. This temporary compound would be<br />
approximately 80m x 50m and would be fenced off from members of the<br />
public during construction activities. The machinery required for the landfall<br />
works are likely to include up to three excavators, a tractor and a winch. The<br />
fenced compound would not extend to the public footpath located landward<br />
of the shingle, and the public would not be prevented from accessing other<br />
parts of the beach that are unaffected by the cabling operations.<br />
6.13.16 Beach anchors would be required during this phase of work, to pull the export<br />
cables to the shore. These would extend approximately 100m to either side<br />
of each cable being pulled. Members of the public would be kept away from<br />
these areas during cable pulling operations, and there would also be security<br />
patrols to ensure that members of the public do not enter these areas. These<br />
temporary beach areas would be located within the existing cable corridor<br />
area shown on Figure 1.2.<br />
6.13.17 Two further areas of HDD are anticipated on the cable corridor route:<br />
underneath the unnamed lane to the west of the transition pits and across<br />
Sizewell Gap. There is also potential to use HDD at other points on the cable<br />
corridor if appropriate. This will be ascertained during the detailed design<br />
phase. Construction methodology and requirements for temporary working<br />
areas will be similar to that set out above.<br />
6.14 Onshore Transition Pits<br />
6.14.1 An onshore transition pit is where each multi-core export cable is jointed to<br />
the single core onshore cables. GWF consists of a maximum of four export<br />
cables, and therefore requires up to four onshore transition pits located<br />
adjacent to each other. The location and dimensions of all four transition pits<br />
together is shown on Figure 1.2. The total footprint of all four transition pits<br />
together would be approximately 16m by 25m. Each pit would be excavated<br />
to a depth of approximately 2m with the only evidence above ground, during<br />
operation, being access covers at ground level for adjacent link boxes.<br />
6.14.2 Each transition pit would be sheet piled and structurally buffered whilst open.<br />
The floor of each transition pit would be concrete lined to provide a flat, clean<br />
working environment. The excavation of the pits would follow environmental<br />
recommendations, with the topsoil being stored separately. At the eastern<br />
end of each transition pit would be the HDD shaft. This would be sealed until<br />
the export cable is ready to be pulled into position. The other end (west)<br />
would be the location from which the four onshore cables would exit towards<br />
the new substation.<br />
6.14.3 The export cables and onshore cables would be jointed together in a<br />
controlled environment, requiring a purpose designed container to be placed<br />
on top of the transition pit.<br />
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6.14.4 Adjacent to each transition pit there would be a link box (up to four in total),<br />
which would be required to be accessible during the operation of GWF. A<br />
link box contains removable links and represents a point where the onshore<br />
and offshore cables can be separated (electrically). This allows a cable fault<br />
to be more easily identified within the onshore or offshore cables. Link boxes<br />
would therefore have a number of surface level access covers and each one<br />
would be placed in the vicinity of its associated transition pit. The area<br />
around the transition pits and link boxes, approximately 30m by 30m, would<br />
be fenced and made inaccessible during operation.<br />
6.14.5 A platform would be required near the onshore transition pits to support<br />
equipment during the cable pull process from shore. This would consist of a<br />
concrete slab approximately 5m by 5m with a shallow structure visible at<br />
surface level. The exact location would be finalised during detailed design,<br />
however a position is likely to be required some 20m beyond the transition<br />
pits in a roughly westerly direction, dependent on the final alignment of the<br />
HDD ducting. It is anticipated that the structure would be removed after<br />
completion of cable installation, although it could be retained within the<br />
fenced transition pit area for operational access.<br />
6.14.6 The total working area for the onshore transition pits would be approximately<br />
75m by 75m and would include space for temporary portacabins, lay down<br />
areas, vehicles and other necessary construction and installation equipment<br />
required during the construction of the transition pit.<br />
6.14.7 A permanent new access track would be required between the transition<br />
pit(s) and Sizewell Gap. The proposed location of this is also shown on<br />
Figure 1.2.<br />
6.15 Onshore Cabling<br />
Onshore cable route<br />
6.15.1 The onshore cable corridor would run between the onshore transition pit and<br />
the GWF 132kV compound, as shown on Figure 1.2.<br />
There would also be two additional cable corridors:<br />
� Between the 132kV/400kV transmission compound and the two<br />
sealing end compounds; and<br />
� Between the 132kV/400kV transmission compound and the existing<br />
National Grid Electricity Transmission (NGET) 132kV cable corridor,<br />
which contains four cables from the Leiston A substation to the<br />
existing 400kV/132kV substation at Sizewell. This connection has<br />
some residual capacity, which is intended to be utilised in the first<br />
instance (i.e. for the first MWh generated) for GWF. Because of<br />
physical constraints it is not practical to extend the existing Leiston A<br />
substation.<br />
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6.15.2 The onshore cabling between the transition pit and the GWF onshore<br />
substation would be approximately 900m in length. The aim would be to<br />
utilise one continuous cable over this distance. However it is possible that<br />
two sections would be required and jointed together. Consideration would be<br />
given to locate any link boxes close to a field boundary to minimise any<br />
impact to agricultural activities. Link boxes would be the only visible indicator<br />
after installation; for safety reasons these areas would be fenced off. The<br />
cable corridor between the 132kV/400kV transmission compound and the<br />
sealing end compounds would be approximately 300m to the western sealing<br />
end compound and 400m to the eastern sealing end compound. The cable<br />
corridor between the 132kV/400kV transmission substation and the existing<br />
NGET 132kV cables would be approximately 300m. The exact route of the<br />
cable corridors will be subject to detailed design and feasibility and will be<br />
subject to micrositing during construction. Preliminary cable corridor routes<br />
are shown in Figure 1.2.<br />
Working area and site preparations<br />
6.15.3 The majority of the cable corridor between the transition pit and the GWF<br />
substation passes through agricultural land under arable cultivation. A 40m<br />
wide working corridor would be required along the length of the cable corridor<br />
where open cut trenching takes place. Figure 1.2 shows the location of the<br />
corridor with a width of approximately 45m to allow for micrositing within the<br />
corridor route if required. The working width would comprise:<br />
� A set of four trenches with a total width of approximately 20m;<br />
� Construction access for vehicles - which needs to allow the safe<br />
tracking of construction vehicles in two directions;<br />
� Topsoil storage (up to 10m in width); and<br />
� Fencing.<br />
6.15.4 The cable corridor between the transmission compound and the sealing end<br />
compounds passes through the northern extent of the Sizewell Wents block<br />
of woodland. A working width of approximately 20m would be required, this<br />
would comprise:<br />
� Cable trenches;<br />
� Construction access for vehicles , which needs to allow the safe<br />
tracking of construction vehicles in two directions;<br />
� Topsoil storage; and<br />
� Fencing.<br />
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6.15.5 The cable corridor between the transmission compound and the existing<br />
132kV cabling passes south of the existing GGOWF substation. A working<br />
width of approximately 20m would be required, this would comprise:<br />
� Cable trenches<br />
� Construction access for vehicles - approximately 8m wide to<br />
allow the safe tracking of construction vehicles in two directions<br />
� Topsoil storage (up to 10m in width)<br />
� Fencing.<br />
6.15.6 The working corridor would be suitably fenced; the type of which would<br />
depend upon the farming activities and discussions with the landowner.<br />
6.15.7 Protection of topsoil would be ensured and the ground reinstated to its former<br />
condition following the construction phase. Generally topsoil would be<br />
stripped from the working corridor using 20t tracked 360 degree excavators<br />
and stored to one side in the area allocated. Topsoil would not be stripped<br />
from the actual storage strip.<br />
6.15.8 In most cases the construction haul road along the working corridor would<br />
require no additional preparation other than topsoil stripping. However in<br />
certain circumstances, such as poor ground conditions, temporary surfacing<br />
such as hardcore, geotextiles or re-useable plastic surfacing may be<br />
necessary.<br />
6.15.9 In some locations it may only be necessary to strip the topsoil from the actual<br />
trench width, with the remaining working corridor being protected by means<br />
of temporary surfaces to protect the underlying soil structure.<br />
Open trench cable installation methodology<br />
6.15.10 Following the cable corridor preparation works, excavation of the cable<br />
trench would commence using a mechanical excavator. The cable trench<br />
width and depth would be approximately 2m by 2m. Dumper trucks would be<br />
used to transport material to and from the storage areas. Any surplus spoil<br />
would be taken off site and disposed of in accordance with the appropriate<br />
waste carrier licence as detailed within the site waste management plan.<br />
Parts of the cable corridor would require some tree felling (through Sizewell<br />
Wents).<br />
6.15.11 Cable installation may be undertaken using a mole plough. This allows the<br />
cable to be installed without the need to dig a trench. As the mole plough is<br />
dragged through the ground, it leaves a channel deep under the ground,<br />
within which the cable is laid.<br />
Reinstatement<br />
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6.15.12 Following completion of the cable system installation, the working area would<br />
be reinstated to its previous condition. This would include:<br />
� Reinstatement of foreshore habitats, including shingle and dune<br />
slacks;<br />
� Reinstatement of topsoil; and<br />
� Reseeding of any fields of grassland, grass margins and ditch<br />
banks.<br />
6.15.13 Table 6.8 provides a summary of the onshore cabling system.<br />
Table 6.8 Summary of the onshore cable system<br />
Key onshore cable system characteristics<br />
Number of cables Up to 4<br />
Transition pit area Approximately 30m x 30m<br />
Total working footprint of transition pits<br />
and link boxes<br />
Onshore Cable length<br />
Link pits, additional to those at the<br />
transition pits (if required)<br />
Trenching technique<br />
Target cable trench depth 1-2m<br />
Cable trench corridor width 20m<br />
Cable trench corridor working width Up to 40m<br />
6.16 Onshore Substation<br />
Approximately 75m x 75m<br />
1,200m (land fall to GWF substation);<br />
300/400m between transmission compound<br />
and sealing end compounds; 300m between<br />
transmission substation and existing 132kV<br />
cables<br />
Up to 4, to be located at a field boundary<br />
Open trench, with HDD proposed for 2 road<br />
crossings and to avoid sensitive foreshore<br />
habitats<br />
6.16.1 The electrical engineering design has identified the need for electrical plant<br />
and equipment to control and facilitate the export of electricity from the wind<br />
farm to the 400kV national electricity transmission network. In order to<br />
achieve this, GWF would require a new 132kV compound to be built near<br />
Sizewell.<br />
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6.16.2 Transmission infrastructure would also be required in order for electricity to<br />
convert from 132kV to 400KV and to reach the existing transmission network.<br />
As such, a 132kV/400kV transmission compound and sealing end<br />
compounds would also be built in the Sizewell area.<br />
6.16.3 The GWF compound and the transmission compound would be located<br />
adjacent to each other and together are referred to as the “GWF substation”.<br />
The GWF substation would be located approximately 1km inland on the<br />
Suffolk coast near Sizewell. It would be situated to the north of Sizewell Gap,<br />
immediately to the west of the existing GGOWF substation site (see Figure<br />
1.2). An aerial view of the existing GGOWF substation is shown in Plate<br />
6.25 to give an indication of the type of equipment that would be present<br />
(note this site does not incorporate lightning protection due to proximity to the<br />
adjacent transmission towers).<br />
6.16.4 The footprint of the GWF substation sits predominantly within arable land<br />
although it also includes part of a block of woodland (Sizewell Wents). In<br />
addition, part of the proposed landscape mitigation area encroaches into<br />
Broom Covert (a block of semi-natural grassland used predominantly for<br />
grazing).<br />
6.16.5 The dimensions of the GWF compound would be approximately 170m by<br />
125m (2.1ha) with a maximum height of approximately 14m, exluding<br />
lightning protection. The dimensions of the transmission compound would be<br />
approximately 70m by 130m (0.91ha) with a maximum height of<br />
approximately 14m, excluding lightning protection. Only a small proportion of<br />
the buildings and equipment in the compounds would be expected to be 14m<br />
in height. In addition, the substation (both compounds) may require a<br />
lightning protection system to be installed to protect the electrical equipment<br />
from lightning strikes. The design of this lightning protection system is<br />
dependent on the equipment that is included within the substation but, if<br />
required, could involve the erection of up to approximately 28 lightning<br />
protection masts, which would each be up to 22m in height, mounted at<br />
ground level. Each mast would have a footprint of approximately 1.5m by<br />
1.5m and would be most likely be in the form of a slim lattice tower design,<br />
although a protective net arrangement is also available. The western sealing<br />
end compound would have dimensions of approximately 32m x 40m (0.1ha)<br />
and the eastern sealing end compound would have dimensions of<br />
approximately 25m by 40m (0.1ha). Gantries would be located in each<br />
sealing end compound which would be used to connect the 400kV cables<br />
from the transmission compound to the adjacent transmission towers<br />
(pylons). The gantries would be approximately 13m in height. Some<br />
modifications to the existing transmission tower cross arms may be required.<br />
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Plate 6.25 Aerial photo of existing GGOWF substation (looking west)<br />
Souce: GGOWFL<br />
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6.16.6 The GWF 132kV compound would comprise up to four electrical bays. The<br />
typical equipment within each electrical bay would include:<br />
� 132kV SF6 switchgear 1 ;<br />
� Transformer;<br />
� Reactive compensation, to include;<br />
� Dynamic reactive compensation, e.g. SVC, STATCOM;<br />
� Mechanically switched capacitors; and<br />
� Mechanically switched reactors.<br />
� Harmonic filters.<br />
6.16.7 The 132kV/400kV transmission compound and associated infrastructure<br />
would include:<br />
� 132kV and 400kV switchgear;<br />
� Two 400kV / 132 kV super grid transformers;<br />
� Control, communication and monitoring equipment; and<br />
� Cable sealing compounds and gantries to connect to the<br />
existing overhead transmission lines.<br />
6.16.8 Each compound would be enclosed by a fence containing the external<br />
equipment outlined above, with the additional features:<br />
� Interconnecting cables;<br />
� Access tracks, gravel paths and hard standing;<br />
� Control buildings;<br />
� Internal substation roads<br />
� Car parking;<br />
� Communications mast;<br />
� Earth mats;<br />
� Lighting;<br />
� Dump tanks;<br />
� Water tanks;<br />
� Back up diesel generators;<br />
� Welfare facilities; and<br />
� Security fencing.<br />
1 switchgear for all bays may be combined and housed in a single building<br />
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6.16.9 Further information regarding the design of the substation and the proposed<br />
landscaping around it is provided in Section 21 Landscape, Seascape and<br />
Visual Character.<br />
6.16.10 Tables 6.9 to 6.11 provide a summary of the onshore infrastructure.<br />
Table 6.9 Summary of the onshore GWF 132kV compound<br />
Key project characteristics<br />
Compound area Up to approximately 2.1ha<br />
Building/electrical equipment height Up to approximately 14m<br />
Number of bays Up to 4<br />
Typical components within each bay<br />
Other substation elements<br />
� 132kV SF6 switchgear 2 ;<br />
� Transformer;<br />
� Reactive compensation, to include;<br />
o Dynamic reactive<br />
compensation, e.g. SVC,<br />
STATCOM;<br />
o Mechanically switched<br />
capacitors; and<br />
o Mechanically switched<br />
reactors.<br />
� Harmonic filters<br />
� Interconnecting cables;<br />
� Access tracks, gravel paths and<br />
hard standing;<br />
� Security fencing<br />
� Up to 16 lightning protection masts<br />
of maximum 22m height<br />
� Earthing mat<br />
� Permanent and temporary utilities<br />
� Control buildings;<br />
� Car parking;<br />
� Communications mast;<br />
� Lighting;<br />
� Dump tanks;<br />
� Water tank;<br />
� Back up diesel generators; and<br />
� Welfare facilities.<br />
2 switchgear for all bays may be combined and housed in a single building<br />
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Table 6.10 Summary of the onshore 132/400kV transmission compound and sealing<br />
end compounds<br />
Key project characteristics<br />
Compound area<br />
Building/electrical equipment height<br />
Typical substation components<br />
Sealing end compounds and gantries<br />
Approximately 0.9ha<br />
Up to approximately 14m<br />
� 132kV and 400kV switchgear;<br />
� Two 400kV / 132 kV super grid<br />
transformers;<br />
� Control building;<br />
� Interconnecting cables;<br />
� Up to 12 lightning protection masts<br />
of maximum 22m height;<br />
� Access tracks, gravel paths and<br />
hard standing;<br />
� Internal substation roads;<br />
� Car parking;<br />
� Earth mat;<br />
� Lighting;<br />
� Dump tanks;<br />
� Water tank;<br />
� Back up diesel generator;<br />
� Welfare facilities; and<br />
� Security fencing<br />
� Total area of 0.2ha; and<br />
� Maximum height of gantries<br />
approximately 13m<br />
� Security fencing<br />
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Table 6.11 Summary of substation permanent and temporary footprint<br />
Development element<br />
Permanent footprint<br />
GWF substation (comprising both compounds) 3.1ha<br />
Sealing end compounds 0.2ha<br />
GWF transition pit 0.1ha<br />
New permanent access roads and turning area 0.3ha<br />
Drainage reserves adjacent to new permanent access roads 0.2ha<br />
Landscape screening area 1.4ha<br />
Security area (5m strip between substation fence and landscape mitigation<br />
area)<br />
Approximate<br />
total area<br />
0.5ha<br />
Total 5.8ha<br />
Temporary footprint<br />
Cable corridor between landfall and GWF compound (working corridor<br />
including transition pit and temporary laydown areas)<br />
400kV cable corridor between transmission compound and sealing end<br />
compounds<br />
132kV cable corridor between transmission compound and joint with<br />
existing Leiston A 132kV cables<br />
Substation and sealing end compounds temporary laydown areas<br />
(excluding land already covered within cable corridor)<br />
6.2ha<br />
0.9ha<br />
0.6ha<br />
10ha<br />
Access roads 0.3ha<br />
Service reserves 0.3ha<br />
Beach compound and access restrictions 1.5ha<br />
Total 17.4ha<br />
6.16.11 Further information regarding the design of the substation and the proposed<br />
landscaping around it is provided in Section 21 Landscape, Seascape and<br />
Visual Character.<br />
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The GWF substation footprint<br />
6.16.12 Although GWF and GGOWF are expected to be of a similar installed capacity<br />
and are located in similar geographical locations there are significant<br />
differences between the two, necessitating an increase in the land included in<br />
the consent application for the GWF substation compared to the GGOWF<br />
substation. The most significant reasons for this necessary increase in size<br />
are listed in the following sections of this chapter.<br />
6.16.13 Unknown reactive power capability of <strong>Wind</strong> Turbine Generators<br />
(WTGs): GGOWF wind farm uses a significant amount of reactive power<br />
from its specific turbines reducing the rating/size of the onshore equipment to<br />
deliver the NGET code/STC obligations. Before final WTG selection for the<br />
GWF project it cannot be assumed that a similar capability will be available<br />
from turbines and that a similar technique will be possible. At this point it is<br />
assumed that turbines will always operate at unity power factor (as per<br />
minimum NGET Code requirement) and all necessary reactive power will be<br />
delivered from the plant onshore. It is expected that the rating of the reactive<br />
compensation for the GWF project may double as compared to the GGOWF<br />
project to cope with these increased requirements.<br />
6.16.14 Different cable parameters: Although GWF is of similar size and location as<br />
GGOWF there may be a significant difference in the final cable parameters<br />
used in both wind farms. The differences may be caused by cable design<br />
(e.g. insulation materials, armouring etc.) and potentially bigger cable size<br />
(i.e. to cope with increased reactive power flow from the wind farm).<br />
Alternative cable parameters may increase charging currents by up to 20%<br />
and necessitate a further increase of the rating of reactive compensation<br />
installations onshore.<br />
6.16.15 Increase in harmonic filters requirements: Accurate specification of<br />
harmonic filters to be installed in the GWF substation onshore can only be<br />
completed once the final parameters of electrical systems (turbines,<br />
transformers, cables, reactive compensation) are available and once the<br />
harmonic injection limits are provided by NGET - the system operator. The<br />
harmonic limits are allocated by the grid operator to projects on the first come<br />
first serve basis. Available harmonic injection limits in the Leiston/Sizewell<br />
location were largely ‘consumed’ by GGOWF project and the remaining<br />
headroom for GWF is expected to be much tighter. It is reasonable to<br />
assume that rating of harmonic filters may increase by 100% - 200% as<br />
compared to the GGOWF project. This will result in a larger area for<br />
harmonic filters in the GWF substation compared to the GGOW substation.<br />
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6.16.16 Alternative technologies: There are various technologies available on the<br />
market to provide the characteristics and functionality required from the GWF<br />
onshore substation. The technologies may differ quite considerably in terms<br />
of size but also capital cost, O&M requirements, system availability, H&S<br />
hazards etc. The technology used in GGOWF project for the reactive<br />
compensation (Siemens SVC +) tends to be on the lower end of the available<br />
options in terms of the footprint requirements, also HIS switchgear used by<br />
Siemens is one of the most compact designs available on the market.<br />
Therefore it has not been assumed that only equipment with the smallest<br />
available footprint will be used as this would curtail both the onshore and<br />
offshore procurement options.<br />
6.16.17 Equipment make: Similarly as per the previous section, equipment of the<br />
same rating and class may differ in size when sourced from alternative<br />
vendors. Based on the experience from other projects, some suppliers tend<br />
to yield a smaller footprint than similar equipment from other manufacturers.<br />
6.16.18 Substation accessibility / maintainability: Given the limited space<br />
available in the GGOWF onshore substation the equipment within the site<br />
was very densely installed. GWF has to achieve acceptable consideration of<br />
health and safety aspects of the development on a risk basis and consider all<br />
practicable options to reduce risk. This includes allowing sufficient space<br />
between the plant, and width of paths and roads within the substation, to<br />
afford safer and easier access to all parts of the system without deenergising<br />
other system components (as has to occur in the GGOWF<br />
substation).<br />
6.16.19 As discussed above there are factors significantly affecting rating and size of<br />
the apparatus to be installed in the GWF onshore substation. It should be<br />
emphasised that the final sizes of equipment and hence the whole substation<br />
have a high degree of uncertainty and it is difficult to estimate accurately<br />
before the technical details of the project become available. Based on<br />
realistically conservative assumptions as to the expected ratings and quantity<br />
of the equipment, GWF has commissioned an indicative design from a major<br />
supplier to develop a draft onshore design for the GWF compound to allow a<br />
realistic estimate of the compound footprint to be calculated. Based on this<br />
work the expected land take for the onshore substation is approximately 1.8 -<br />
2ha (i.e. about 3.6 - 4 times footprint of the equivalent compound in the<br />
GGOWF onshore substation).<br />
6.16.20 The size of the transmission compound which will be used to connect GWF<br />
to the onshore transmission network is also expected to increase in size as<br />
compared to the substation serving GGOWF (called Leiston A). NGET<br />
utilises the pre-existing super grid transformers (SGTs) and 400kV<br />
switchgear located within Sizewell B power station for the GGOWF<br />
connection but this infrastructure has insufficient spare capacity to<br />
accommodate the expected output of GWF and therefore additional SGTs<br />
and switchgear would be required within the new transmission compound, as<br />
well as the 132kV switchgear that was required for GGOWF.<br />
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6.16.21 The SGTs and 400kV equipment will be located within the same compound<br />
as the 132kV switchgear, increasing the size of the transmission compound<br />
by approximately 100 - 150%.<br />
6.17 <strong>Project</strong> Programme<br />
6.17.1 The key project programme details are detailed in Table 6.12. The dates<br />
may be subject to change, but provide the current best estimate to enable a<br />
meaningful assessment to be made at this juncture.<br />
6.17.2 As the offshore wind farm industry is developing rapidly, a number of the key<br />
components are in high demand. In addition, several components have long<br />
lead times such as the subsea export cables and the main transformers<br />
which can take up to 18 months to be manufactured. Therefore production<br />
slots have to be booked several years in advance to secure these items.<br />
This is an important consideration, as it sequentially shapes and drives the<br />
overall programming of works and the selection of components of the<br />
scheme.<br />
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Table 6.12 Indicative project programme<br />
Timing 2012 2013 2014 2015 2016 2017<br />
Detail<br />
Achieve consent<br />
Grid construction<br />
Q4 Q1 Q2 Q3 Q4 Q1 Q2 Q3 Q4 Q1 Q2 Q3 Q4 Q1 Q2 Q3 Q4 Q1 Q2 Q3<br />
3<br />
Offshore<br />
foundations 4<br />
Offshore cables 5<br />
Offshore<br />
topsides 6<br />
Commissioning<br />
and handover<br />
<strong>Project</strong><br />
completion<br />
3 Encompasses all onshore sub-station construction, cable installation and NGET transmission system works<br />
4<br />
Includes all WTG and ancillary infrastructure foundations<br />
5<br />
Includes export, inter and interra-array cable works<br />
6<br />
Includes all WTG components and topsides of ancillary infrastructure<br />
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6.18 Offshore Pre-construction and Construction<br />
6.18.1 Construction of the offshore works would generally be completed in a number<br />
of stages, which are as follows:<br />
� Pre-construction surveys<br />
� Prefabrication (structures constructed onshore)<br />
� Transportation (structures floated or transported by<br />
transportation vessels)<br />
� Offshore foundation structure installation<br />
� Offshore substation installation and commissioning<br />
� Inter and intra-array cabling<br />
� Transitional pieces installed<br />
� WTG installation<br />
� Cable landfall works<br />
� Export cabling<br />
� Commissioning.<br />
6.18.2 Installation of the offshore elements would primarily take place outside of the<br />
winter months due to the potential adverse weather conditions, which<br />
increases the risk of delays in activities and excessive costs. The main<br />
offshore construction season may extend from March to November each year<br />
depending on the vessels chosen by the construction contractor, although<br />
consideration would still be given to working outside of this envelope if<br />
practicable and safe. Offshore construction works would normally be carried<br />
out on a 24 hour operations basis.<br />
6.18.3 A two season programme is likely to be adopted. In the first season<br />
installation would also include all of the navigational aids required to ensure<br />
navigational safety, as laid down in the appropriate guidelines (see Chapter<br />
17). The commissioning programme would then take place throughout both<br />
construction seasons, as the WTGs would be brought online sequentially.<br />
6.18.4 The project timetable would ensure that any seasonal restrictions on certain<br />
activities identified during the consenting process are adhered to. Subject to<br />
all consents for the project being received during late 2012, it is anticipated<br />
that GWF project would be constructed in 2013 – 2016 though this would be<br />
influenced by a number of factors.<br />
6.18.5 Table 6.13 summarises the indicative suite of construction vessels and<br />
vehicles that would be utilised for the construction of offshore components of<br />
GWF.<br />
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Table 6.13 Construction activity summary<br />
Construction<br />
aspect<br />
Pre-construction<br />
geophysical survey<br />
Pre-construction<br />
geotechnical survey<br />
Detail<br />
Dedicated geophysical survey vessel using side scan sonar,<br />
multibeam echosounder and magnetometer. Would survey GWF site,<br />
export cable corridor and landfall site.<br />
Dedicated geotechnical survey vessel taking a number boreholes,<br />
cone penetration tests (CPT) and vibrocores within the GWF site,<br />
export cable corridor and landfall site.<br />
Pre-lay grapnel run Dedicated vessel with PLGR device and ROV<br />
Plough trails Cable installation vessel along selected installation equipment<br />
(plough, jetting ROV and or trencher).<br />
WTG and ancillary<br />
infrastructure<br />
foundations<br />
Foundation installation HLV / jack-up barge, possible grouting vessel,<br />
possible foundation transportation vessel and opossible support<br />
vessels<br />
.<br />
Scour protection Construction barge or dedicated rock placement vessel<br />
WTGs HLV or jack-up barge<br />
Ancillary structures<br />
(OSP, collection<br />
station,<br />
accommodation<br />
platform and met<br />
mast)<br />
HLV or jack-up barge, substation installation vessel<br />
Cable lay Cable lay barge/ vessel<br />
6.18.6 The physical footprint on the seabed from the construction vessel activity<br />
would come from a number of sources including PLGR work, jack-up barge<br />
legs, anchor placement (if DP vessels not used), cable<br />
plough/trencher/jetting machine and would be dependent on the method<br />
utilised and the number of movements required (dictated by the WTG option<br />
taken forward and site layout). A jack-up barge would have between four<br />
and six legs with a footprint of around 30m 2 per leg. The anchor vessels<br />
would have between four and six anchors each, with the anchor size being<br />
around 2-4m 2 .<br />
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6.18.7 In addition to these main vessel movements, there would also be significant<br />
levels of activity undertaken by smaller support vessels, including:<br />
� Tow barges<br />
� Anchor handling tugs<br />
� Offshore supply vessels<br />
� Crew vessels for personnel / equipment transfer<br />
� Standby vessels<br />
� Guard vessels.<br />
Construction logistics, management and security<br />
6.18.8 During marine operations a Safety Zone would be applied for the<br />
construction, commissioning and operational phases of the project.<br />
6.18.9 The purpose of a safety zone would be to manage the interaction between<br />
vessels and the wind farm in order to protect life, property and the<br />
environment. The fundamental principle is that vessels would be kept at a<br />
safe distance from construction, commissioning and operational activities<br />
related to the wind farm in order to avoid collisions.<br />
6.18.10 A 500 metre safety zone (the maximum permissible under international law)<br />
is very likely to be in place around each turbine during the construction<br />
phase. The safety zone would be monitored and controlled by the <strong>Project</strong><br />
with the support of a Marine Control Centre.<br />
6.18.11 During construction, wind farm extremities are generally marked with<br />
standard cardinal marks, and in areas of high traffic density guard vessels<br />
may also be employed. The requirement for such measures are set out in<br />
the International Association of Lighthouse Authorities (IALA)<br />
Recommendation O-117 on ‘The Marking of Offshore <strong>Wind</strong> <strong>Farm</strong>s’ (as<br />
detailed under Section 6.23 below). Jack-up barges and HLV whilst<br />
‘engaged’ in construction work would be lit in line with the requirement of<br />
IALA Recommendation O-114 on the Marking of Offshore Structures.<br />
Specific detail on that proposed for GWF is provided in Chapter 17 Shipping<br />
and Navigation.<br />
Pollution prevention<br />
6.18.12 Pollution prevention would be controlled and mitigated from the design stage<br />
onwards. For example, the WTG nacelle frame would typically be designed<br />
and manufactured with a bund incorporated which can hold the full oil content<br />
of the gearbox in the event of catastrophic failure. Additionally, if any oil filled<br />
transformers are used, again the area would be bunded to contain any oil<br />
leaks (as discussed in Section 6.9 and 6.10).<br />
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6.18.13 The staff and vessel crew would be trained and equipped to use spill kits in<br />
the event of a break in containment occurring. This would be defined by<br />
GWFL at the appropriate juncture and would be governed by a full Risk<br />
Assessment and Method Statement process additionally the work relating to<br />
the WTG would specifically be controlled and managed via the <strong>Wind</strong> Turbine<br />
Safety Rules .<br />
6.18.14 There would also be a waste management procedure which would be<br />
administered and managed to ensure it is strictly adhered to by site staff,<br />
contractors and visitors to the wind farm.<br />
6.18.15 In the event of the safe system of work failing or a catastrophic incident<br />
occurring it is assumed that a spill response contract would be in place to<br />
control, manage, recover and dispose of any contaminants and dropped<br />
objects.<br />
Construction ports<br />
6.18.16 GWFL are not in a position to make commitments with regard to specific<br />
ports at this stage. The construction ports used for the GWF project would<br />
be driven by the contractual placements for the wind farm components and<br />
availability of sufficient port space.<br />
6.18.17 It is envisaged that a local port would be selected by the GWF project<br />
principal contractor based on suitability for facilitating the transportation<br />
vessels, equipment to move the wind farm components and skilled labour<br />
force, if secondary fabrication is required. The port would require the<br />
necessary space to layout a production line to fit the components, have a<br />
large volume of storage space and be able to accommodate deep water draft<br />
construction vessels.<br />
6.18.18 The location of other ports associated with the construction process would be<br />
driven by the location of the chosen manufacturing companies for the various<br />
components associated with the wind farm. Experience from Round 1 and 2<br />
projects indicates that this diversity may be at a global scale.<br />
6.19 Onshore Construction<br />
Construction sequence and timing<br />
6.19.1 Onshore, the construction programme is based on a likely 32 month<br />
programme. The construction sequence and approximate length of each is<br />
shown in Table 6.14.<br />
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Table 6.14 Onshore construction timings<br />
Activity Duration<br />
Site preparation 6 months<br />
Construction of both substations 24 months<br />
Onshore cabling 8 months<br />
Transition pit 3 months<br />
HDD works 4 months<br />
Site demobilisation 3.5 months<br />
6.19.2 It is estimated that the onshore construction workforce would not exceed 200<br />
personnel during the peak construction period. Onshore working shifts are<br />
anticipated to be 08:00 to 19:00 from Monday to Friday; and 09:00 to 13:00<br />
on Saturday. Construction activity may occasionally require 7 days per<br />
week. Where the working hours are expected to extend beyond those given<br />
above, these periods would be agreed in advance with the Local Planning<br />
Authority to ensure that they do not clash with programmed community<br />
activities such as village fetes. The following activities could result in an<br />
extended working week:<br />
� Continuous concrete pours, which would generally occur nearer<br />
the start of the civil construction phase<br />
� Weather window during a spate of bad weather<br />
� Testing of equipment.<br />
6.19.3 It is noted that the above work timing does not apply to works related to cable<br />
landfall in the intertidal zone, where working hours would be dictated to a<br />
large extent by the tidal state.<br />
Site preparation and earthworks<br />
6.19.4 The site boundary would be securely fenced using a suitable steel mesh and<br />
panel fencing system. A construction compound would be located within the<br />
site boundary. This would include contractor’s offices / cabins plus an<br />
equipment storage area.<br />
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6.19.5 Earthworks would be required in order to create a level area upon which the<br />
substation would be built, which would generate spoil. Excavated material<br />
would be used as part of the site landscaping wherever possible, however<br />
this may not account for all the material generated. Should additional spoil<br />
be taken off site this would be done in accordance with the agreed site waste<br />
management plan.<br />
6.19.6 It is estimated that this phase of the civil engineering works would take<br />
approximately 6 months to complete.<br />
Building construction works<br />
6.19.7 The substation buildings would most likely be constructed immediately<br />
following the initial civil engineering works, with an estimated timescale of 24<br />
months.<br />
Earthworks and planting<br />
6.19.8 The remaining programme of topsoil reinstatement and planting works would<br />
be implemented to visually contain the new substation and sealing end<br />
compounds. Full details are provided in Section 21 Seascape, Landscape<br />
and Visual Character.<br />
Traffic and access<br />
6.19.9 Table 6.15 provides a provisional estimate of the vehicle movements<br />
required during the construction of both the GWF and transmission<br />
compounds and associated infrastructure. This predicts not only the delivery<br />
of major plant items but also the daily travelling of the workforce, based on<br />
current assumptions.<br />
Table 6.15 Summary of construction related traffic<br />
Key traffic<br />
Site preparation 315 lorries (630 movements)<br />
GWF Substation 2650 lorries (5300 movements)<br />
Onshore cabling 300 lorries (600 movements)<br />
Transition pit 30 lorries (60 movements)<br />
HDD works 100 lorries (200 movments)<br />
Site demobilisation 213 lorries (426 movements)<br />
Max daily workforce<br />
200. Therefore assume 150 cars per day<br />
(300 movements)<br />
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6.20 Commissioning<br />
6.20.1 To ensure that the electrical energy from GWF is delivered to the national<br />
400kV transmission system, three parties must ultimately operate the assets<br />
applied for in the GWF consent. These three parties are GWF, NGET (the<br />
operators of the 400kV network, and the offshore transmission owner<br />
(OFTO), which is the new regulatory regime for licensing offshore electricity<br />
transmission.<br />
6.20.2 The GWF project, as described within this chapter, can be split into the<br />
following systems or components, from which follows a description of the<br />
commissioning process and associated parties responsible:<br />
� Transmission grid connection;<br />
� Onshore GWF substation;<br />
� Export cables;<br />
� Offshore platform substation;<br />
� OFTO Supervisory Control And Data Acquisition (SCADA) system;<br />
� Array cables;<br />
� Equipment within transition pieces (if TPs are installed);<br />
� Balance of Plant SCADA system;<br />
� <strong>Wind</strong> Turbine Generators; and<br />
� <strong>Wind</strong> SCADA.<br />
6.20.3 NGET would be responsible for the transmission grid connection<br />
commissioning, whilst the OFTO would take responsibility for the onshore<br />
GWF substation, export cables, offshore platform substations and the<br />
associated OFTO SCADA system.<br />
6.20.4 The GWF project principal contractor would manage the delivery of the<br />
commission programme associated with the array cables, equipment within<br />
the transition pieces (if TPs are installed) and the balance of plant SCADA.<br />
6.20.5 The array cables transport the electrical energy onto the offshore platform<br />
substations, were an assortment of MV equipment manages the electricity<br />
prior to it reaching the OFTO interface point. The GWF project principal<br />
contractor would also be responsible for the commissioning this MV<br />
equipment. This leaves the GWT WTG and the wind SCADA to be<br />
commissioned by the appointed wind turbine manufacture.<br />
6.20.6 Commissioning would generally be made up of the following process, with<br />
procedures formalising the different stages:<br />
� A mechanical, visual and electrical continuity assessment;<br />
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� An energisation programme;<br />
� Testing mechanical, electrical and control functions;<br />
� Identification of faults;<br />
� Rectification of faults;<br />
� Re-testing; and<br />
� Certification.<br />
6.20.7 The commissioning of GWF would be in accordance with approved<br />
commissioning procedures and would include the NGET commissioning<br />
procedures where applicable. All commissioning activities would be the<br />
subject of an approved safe system of work. Commissioning activities would<br />
include the WTG’s performance and reliability testing and compliance with<br />
the grid code standard.<br />
6.21 Offshore Operations and Maintenance<br />
Overview<br />
6.21.1 All elements of the onshore and offshore GWF project would be designed to<br />
operate unmanned with the systems monitored and instructions issued from<br />
a central location 24 hours a day.<br />
6.21.2 The wind farm and associated plant and apparatus would be controlled and<br />
monitored centrally using SCADA systems, most likely located with in the TP.<br />
The SCADA systems are the means by which the monitoring is undertaken<br />
and commands relayed to the equipment.<br />
6.21.3 The facility would also exist for starting and stopping of WTG in events such<br />
as emergencies or access to the turbines by helicopter for hoisting personnel<br />
onboard.<br />
6.21.4 The WTG would normally shut down during severe weather conditions, when<br />
wind speeds exceed 25ms -1 to avoid damage to the turbine components.<br />
6.21.5 Planned outages for a WTG would be triggered primarily by routine<br />
maintenance requirements, but also occasionally at the request of the<br />
Maritime Rescue Co-ordination Centre (MRCC) in support of Search and<br />
Rescue (SAR) activities in the area.<br />
Operational safety zones<br />
6.21.6 It is likely, although to be confirmed, that an operational safety zone of 50m<br />
around each structure would be applied for. Furthermore, during<br />
maintenance operations this would be extended to 500m (the maximum<br />
permissible under international law) around the relevant structures.<br />
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6.21.7 The control mechanisms and processes associated with the operational<br />
phase would be as specified under construction details.<br />
6.21.8 Once the <strong>Wind</strong> <strong>Farm</strong> is in operational use, an Automatic Identification<br />
System (AIS) as well as CCTV from control centre may be used to monitor<br />
vessel movements within the wind farm.<br />
WTG navigation aids and lighting<br />
6.21.9 As with the construction phase, the marking of the wind farm would be in<br />
accordance with the requirements set out in the IALA Recommendation O-<br />
117 on ‘The Marking of Offshore <strong>Wind</strong> <strong>Farm</strong>s’ and IALA Recommendation O-<br />
114 on the marking of offshore structures. Under these recommendations<br />
the following would be of relevance for GWF:<br />
� Navigation aids would be fitted on any WTG below the lowest point of<br />
the arc of rotation of the turbine blades, and at a height above HAT of<br />
not less than 6m or more than 15m, typically at the top of the yellow<br />
section of the mast.<br />
� Corner or significant boundary point WTGs would be designated a<br />
Significant Peripheral Structure (SPS), with a minimum separation<br />
distance of 3nm between SPS’s. Each SPS would be fitted with lights<br />
that are visible from all directions in the horizontal plane, and the lights<br />
on a structure should be synchronised to show a yellow ‘special mark’<br />
light characteristic with a range of not less than 5 nautical miles.<br />
� Intermediate Peripheral Structures (IPS) may be used between SPS.<br />
These would be within 2nm of SPS, and fitted with lights as per SPS,<br />
but with a distinct flash characteristic. They would be visible from a<br />
minimum range of 2nm.<br />
6.21.10 Additional aids to navigation would be at the discretion of the operator, and<br />
may include:<br />
� Racons, which may have morse letter ‘U’ or radar reflectors;<br />
� AIS; and<br />
� Sound signals may be fitted for restricted visibility with a range of not<br />
less than 2 nautical miles.<br />
6.21.11 Ancillary structures would be marked in accordance with IALA<br />
Recommendation O-114 on the Marking of Offshore Structures.<br />
6.21.12 Individual WTG would be marked with a unique alphanumeric identifier which<br />
would be clearly visible at a range of not less than 150m. At night, the<br />
identifier would be lit discretely (e.g. with down lighters).<br />
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Operation and maintenance activities<br />
6.21.13 O&M of the wind farm after commissioning would comprise both scheduled<br />
and unscheduled maintenance events. Scheduled works on the WTG and<br />
onshore/offshore electrical infrastructure would include annual or bi-annual<br />
maintenance and inspection visits. In addition, necessary retrofitting and<br />
upgrading works may also take place. The scheduled works would normally<br />
be timetabled for the summer months, given the typically more settled<br />
weather and longer day light hours. During this period, O&M personnel at<br />
site would be expected to peak, consisting of up to 30 technicians and eight<br />
vessel crew aboard four vessels.<br />
6.21.14 Unscheduled repair activities would range from attendance on location to<br />
deal with the resetting of false alarms to major repairs. The frequency of<br />
unscheduled activities would be expected to be highest in the early years of<br />
operation (one visit per turbine, per month) when experience on other wind<br />
farms sites has shown the highest number of teething faults tend to occur.<br />
After the first two years of operation, unscheduled visits to turbines would be<br />
assumed to reduce in frequency to six month intervals.<br />
Access strategy<br />
6.21.15 Access to each installation offshore would be by boat or helicopter with at<br />
least two service personnel being on each offshore structure at any one time<br />
for safety reasons. In order to achieve the maintenance programme, it is<br />
anticipated that O&M teams would work simultaneously on several WTG<br />
(and potentially also on the offshore substations). It is therefore expected<br />
that, when boat access is required, at least two vessels would be on-station<br />
within the wind farm site at all times that O&M work is being undertaken.<br />
6.21.16 GWFL would consider the use of both boats (currently using aluminium<br />
catamarans known as windcats) and helicopters when establishing a suitable<br />
access strategy. The boats may be used for routine maintenance operations<br />
and in weather conditions up to approximately 2m wave height. Helicopters<br />
may be used in situations which are time crucial and for increasing access<br />
when vessels are unable to work.<br />
6.21.17 GWFL may also explore the potential need for the use of a mothership, such<br />
a vessel typically serves to accommodate the personnel, provides a control<br />
room facility and acts as the main stores location for the site. They are also<br />
commonly fitted out with a number of work boats and associated launch and<br />
recovery systems. Latest mothership vessel designs also incorporate ROV,<br />
diver operations and helicopter pads and are therefore able to service much<br />
of the post construction and asset management work that would be required<br />
over the life of the project.<br />
6.21.18 The primary means of transferring personnel would be via the workboats<br />
which may be stationed with the mothership (if utilised), but this would also<br />
be supplemented by helicopter support.<br />
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6.21.19 Detailed evaluation is underway to identify the best access strategy for GWF.<br />
It would consider the extension of existing GGOWL services to cover the<br />
GWF project.<br />
Maintenance team<br />
6.21.20 GGOWF already have an Operational Team in place for the day to day<br />
management and control of their project. The GGOWF Operational Team<br />
are based in a purpose built facility situated on the key side at Lowestoft.<br />
This is also the location of the maintenance transportation vessel. The<br />
operation and maintenance activities have already been scoped, plans<br />
developed and necessary services procured. In addition, call off orders are<br />
already in place with companies who can provide specialist vessels or<br />
equipment that might be required at short notice in the event of a failure.<br />
6.21.21 Further investigation is presently being undertaken to assess the suitability of<br />
the GGOWF work remit and services being extended to include the GWF<br />
project as it enters its working phase.<br />
6.21.22 The OFTO would be responsible for the offshore substations and the export<br />
cables. Once appointed it would be their decision on the exact numbers of<br />
full time service personnel, the marine access options to be used and their<br />
base location.<br />
Offshore accommodation<br />
6.21.23 The addition of an accommodation platform could facilitate the mobilisation of<br />
maintenance crew for short durations or in an emergency, adding a degree of<br />
further flexibility to the maintenance strategy. Further detailed analysis would<br />
be undertaken to evaluate the benefits of the accommodation platform before<br />
the final decision is taken on its appropriateness. GWFL would explore all<br />
possible accommodation options, if required, including a fixed platform,<br />
floating hotel and jack-up vessel for transferring and accommodating<br />
maintenance staff.<br />
6.21.24 The supply logistics for the fixed platform/floating hotel/jack-up operating as<br />
the operations and maintenance hub, would be managed by the onshore<br />
O&M base, with an offshore supply vessel used to replenish the<br />
accommodation facility with food, water (if necessary), fuel, spares and<br />
equipment on a regular basis to meet operational requirements<br />
Operation and maintenance port and facilities<br />
6.21.25 The GGOWF project has utilised Lowestoft, in Norfolk, and it is noted that<br />
this facility has additional space which could be converted to accommodate<br />
GWF. However, as for construction, the O&M port is under consideration,<br />
with an independent port study current being undertaken.<br />
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6.21.26 The O&M base would need to be able to provide facilities for the O&M crew,<br />
control centre for the operations, storage space for maintenance equipment<br />
and spare parts, and some strategic spare parts such as gearboxes,<br />
generators, and possibly blades.<br />
6.21.27 It is also likely that a telecommunication mast would have to be erected as<br />
part of the O&M base infrastructure to communicate with the wind farm<br />
personnel and the associated transport. Typically the mast could be<br />
approximately 18m high and be used for VHF telecommunications and<br />
microwave line of site communications if used.<br />
6.21.28 The chosen O&M facility would be equipped with a chart indicating the GWF<br />
projects WTG displaying their unique identification numbers, in accordance<br />
with MGN 371 (M+F).<br />
6.21.29 It would be possible for each individual WTG to be remotely controlled from<br />
the O&M facility. This would enable WTG to be controlled and shut down at<br />
the request of the MRCC in support of SAR activities in the area. These<br />
procedures would be tested on a regular basis, in accordance with MGN 371<br />
(M+F). Furthermore, the WTG would be remotely monitored on a 24 hour<br />
basis from the WTG manufacturer’s control room. The above is discussed in<br />
more detail in Chapter 17. Any port works falling under the remit of the<br />
Planning Act, the Town and Country Planning Act or other relevant planning<br />
legislation do not form part of the GWF application.<br />
6.22 Onshore Operations and Maintenance<br />
Cable route overview<br />
Operation<br />
6.22.1 Once operational the onshore cable system would be primarily beneath the<br />
ground surface and buried to a sufficient depth to allow ploughing and other<br />
agricultural practices to continue. The only above ground features would be<br />
related to the onshore transition pit if required. This would preferentially be<br />
located at a boundary feature, which would minimise the impact to farming<br />
activities.<br />
Maintenance<br />
6.22.2 A full check of the cable system would be carried out on an annual basis.<br />
Access would normally be along the agreed cable route wayleave by foot.<br />
Fault repairs<br />
6.22.3 In the unlikely event that there is any failure of cables, a fault finder with test<br />
gear would locate the fault along the cable section. Once located, the area<br />
around the fault would be excavated and the fault repaired. If the cable<br />
cannot be repaired, a new length of cable would be inserted and jointed to<br />
replace the failed section.<br />
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Substation overview<br />
Operation and maintenance<br />
6.22.4 It is not anticipated that the new substation would be permanently manned<br />
but maintenance and inspection visits would occur.<br />
6.22.5 In summary, the main equipment at the site would consist of transformers,<br />
electrical reactors, capacitors, and switchgear. Best practice guidelines for<br />
the frequency of maintenance of this equipment is summarised in Table 6.16,<br />
and would be adhered to during the lifetime of the operational phase.<br />
Table 6.16 Maintenance required at substation<br />
Equipment Maintenance<br />
frequency<br />
Transformer /<br />
electrical reactor<br />
Routine – annually<br />
Intermediate – four<br />
years<br />
Major – 12 years<br />
Type of work<br />
� Check silica gel and ventilator,<br />
check for oil leakage, check cooling<br />
equipment, general visual<br />
inspection;<br />
� Test for water content, dielectric<br />
strength, acidity and dissolved gas<br />
analysis; and<br />
� Clean bushings and grease<br />
ventilator.<br />
Capacitors Routine – annually � General visual inspection.<br />
GIS / AIS switchgear Routine – annually<br />
Intermediate – six<br />
years<br />
� Check gas pressure, check and<br />
clean mechanisms and hydraulics;<br />
and<br />
� Test protection and control<br />
equipment.<br />
6.22.6 It is envisaged that the maintenance works would normally only require a site<br />
visit by a light goods vehicle (LGV). Any major equipment failure<br />
necessitating removal would require the use of suitable mobile cranes.<br />
Utilities and environmental issues<br />
6.22.7 Potable water for drinking and washing would be provided by a permanent<br />
connection to the local mains water network. Wastewater disposal from site<br />
would be either facilitated by a permanent connection to the local sewer<br />
network or via a septic tank.<br />
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6.22.8 Surface water drainage options would be developed based on an<br />
understanding of the area of impermeable surfaces being created and known<br />
soil infiltration rates. The drainage plan would ensure that the surface water<br />
run-off rate of the new development would be maintained at the existing<br />
‘greenfield’ rate. Sustainable Drainage Systems would be preferred and<br />
would be expected to include, permeable paving, swales, and other water<br />
attenuation techniques. The risk to water quality from pollution sources at<br />
the station is considered to be low. Surface water quality would be protected<br />
by the following measures:<br />
� Oil retention bunds around the transformers, reactors and any<br />
other oil filled equipment that may be used; and<br />
� Oil interceptors on the surface water drainage gullies.<br />
6.22.9 The transformers and electrical reactors would be filled with mineral<br />
insulating oil and would be located within bunds to contain any leakage. The<br />
capacitors are sealed units and contain non-PCB, biodegradable insulation<br />
liquid. The switchgear would be constantly monitored for gas pressure to<br />
detect any leakage.<br />
6.22.10 Transformers, electrical reactors and associated cooling equipment would<br />
comply with NGET noise level specifications measured in accordance with<br />
IEC 60076-10. Where additional noise mitigation measures would be<br />
required, and where these would not be achieved through distance<br />
attenuation or baffling by site screening, consideration would be given to<br />
employing noise attenuation housings around equipment where practicable.<br />
Noise impacts are considered within Chapter 27 Noise.<br />
6.22.11 It is not envisaged that the site would be provided with permanent lighting<br />
around the internal roads or equipment. Lighting may be provided at the<br />
main entrance doors for safe ingress / egress to the buildings. In the event of<br />
any essential works, temporary task lighting would be provided by the<br />
maintenance staff in addition to any installed lighting use.<br />
Operational safety zones<br />
6.22.12 The onshore substation site would have a security fence surrounding its<br />
perimeter. Access beyond the entrance at Sizewell Gap would not be<br />
possible. Beyond this there are no formal operational safety zones<br />
envisaged for GWFL.<br />
6.23 Repowering<br />
6.23.1 The wind farm’s operational life is defined (by The Crown Estate) as up to 25<br />
years, an additional two years would be granted to the lease to allow<br />
decommissioning to take place. All elements of the wind farm would be<br />
designed with a minimum operational life of 25 years.<br />
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6.23.2 Following this a decision would be made on whether the operating company<br />
wish to proceed with decommissioning or apply to the relevant Regulatory<br />
Authority at the time, to repower the wind farm.<br />
6.23.3 Should repowering be sought then an investigation would be undertaken as<br />
to the possible options for this. It is envisaged that any such repowering<br />
activity would require a new agreement for lease with The Crown Estate and<br />
would be subject to an additional planning consent application.<br />
6.23.4 It is acknowledged within the Scoping Opinion for GWF that the statutory<br />
nature advisory body (the Joint Nature Conservation Committee, JNCC) has<br />
requested (on Pg 5 of their response) that:<br />
“It is important to be clear on what repowering entails and whether there<br />
is likely to be any relocation of subsea infrastructure or alteration of the wind<br />
farm layout. This includes whether further scour protection is required for<br />
foundations in the same, or in new, locations across the wind farm site. Any<br />
alterations to the locations of offshore elements for repowering may require<br />
an update to the benthic survey work and assessments that have previously<br />
been carried out”.<br />
6.23.5 GWFL are not able to make such detailed statements with regard to<br />
repowering at this stage. GWFL do however, commit to working closely with<br />
the Government’s advisory bodies throughout the life cycle of the project and,<br />
should at any stage repowering be considered, progressing detailed dialogue<br />
covering how such matters would take place.<br />
6.24 Decommissioning<br />
6.24.1 A full Decommissioning Plan for the project would be drawn up and agreed<br />
with the Department for Energy and Climate Change (DECC) before<br />
construction commences.<br />
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6.25 References<br />
DONG energy, (2009). The Monopod Bucket Foundation; Recent experience<br />
and challenges ahead. Presentation at Offshore <strong>Wind</strong> 2009<br />
DOWL, (2009). Dudgeon Offshore <strong>Wind</strong> <strong>Farm</strong>: Environmental Statement.<br />
DOWEC, (2003). Suction bucket foundation. Feasibility and pre-design for<br />
the 6 MW DOWEC<br />
GGOWL, (2009). Cable laying and landfall plan<br />
GGOWL, (2011). Greater Gabbard Construction Method Statement<br />
Ibsen, L.B., Liingaard. M., Nielsen, S. A, (2005). Bucket Foundation, a status.<br />
Jim Hodder Associates. (2010). <strong>Galloper</strong> <strong>Wind</strong> <strong>Farm</strong>: Cable Desktop Study.<br />
Report C1001\101130<br />
Subacoustech, (in prep). Underwater noise modelling for the <strong>Galloper</strong> <strong>Wind</strong><br />
<strong>Farm</strong><br />
Nedwell J R, Turnpenny A W H, Lovell J, Langworthy J W, Howell Dm and<br />
Edwards B. (2003). The effects of underwater noise from coastal piling on<br />
salmon (Salmo salar) and brown trout (Salmo trutta). Subacoustech report to<br />
the Environment Agency<br />
Nedwell J R, Parvin S J, Edwards B, Workman R, Brooker A G and Kynoch J<br />
E (2007) Measurement and interpretation of underwater noise during<br />
construction and operation of offshore windfarms in UK waters.<br />
Subacoustech Report No. 544R0738 to COWRIE Ltd<br />
Parvin S J and Nedwell J R. (2006). Underwater noise survey during impact<br />
piling to construct the Barrow Offshore <strong>Wind</strong> <strong>Farm</strong>. COWRIE <strong>Project</strong> ACO-<br />
04-2002<br />
The Crown Estate, (2010). A guide to an Offshore <strong>Wind</strong> <strong>Farm</strong>.<br />
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