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Review of Cabling Techniques and Environmental Effects Applicable

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Physical change<br />

along the cable route <strong>and</strong> reduce to less than 20 mg/l within 1000ft <strong>of</strong> the cable<br />

route.<br />

It is interesting to note that the results <strong>of</strong> the above modelling exercise completed<br />

in the USA are broadly in agreement with the modelling <strong>and</strong> site measurements<br />

discussed above for a number <strong>of</strong> wind farms in the UK.<br />

4.5.3 CONCLUSIONS AND FURTHER RESEARCH<br />

The findings from the studies undertaken for a number <strong>of</strong> UK <strong>of</strong>fshore wind farms<br />

indicate that the disturbance to seabed sediments during cable burial operations<br />

are likely to be short term <strong>and</strong> relatively localised, particularly if ploughing<br />

techniques are employed. It is unlikely that cumulative or in-combination<br />

impacts will present significant problems because <strong>of</strong> the short term nature <strong>of</strong><br />

the burial operations.<br />

As noted earlier there is limited research <strong>and</strong> advice on the quantification <strong>of</strong><br />

material arising from cable burial operations, particularly if jetting, dredging or<br />

cutting/excavating methods are adopted. This lack <strong>of</strong> base information on the<br />

release <strong>of</strong> sediment into suspension limits the benefits that could arise from the<br />

use <strong>of</strong> more sophisticated modelling techniques to establish the fate <strong>of</strong> released<br />

sediment. It is, therefore, suggested that this is an area where further research<br />

would be <strong>of</strong> value. It is appreciated that monitoring requirements included in<br />

FEPA licences for UK Round 1 <strong>and</strong> 2 <strong>of</strong>fshore wind farms will provide valuable<br />

data for the quantification <strong>of</strong> the impacts <strong>of</strong> cable burial operations.<br />

4.6 Mitigation Measures<br />

The previous sections have discussed the influence <strong>of</strong> cable burial operations<br />

on sediment disturbance. In practice the main areas where mitigation measures<br />

can be adopted to reduce this disturbance are during the selection <strong>of</strong> the cable<br />

route <strong>and</strong> cable burial method. Both the route <strong>and</strong> burial methods adopted will<br />

be a balance between the engineering issues associated with the route corridor<br />

(see Section 3.10 on the Burial Assessment Surveys) <strong>and</strong> the key environmental<br />

issues associated with the site. The range <strong>of</strong> environmental issues likely to be<br />

encountered is discussed in Section 5.<br />

An appropriate level <strong>of</strong> site investigation (see Section 4.2.1) is an essential to<br />

ensure that the optimum route <strong>and</strong> burial methods are selected for the cable.<br />

The level <strong>of</strong> data gathered should be sufficient to provide confidence in the<br />

selected route <strong>and</strong> burial method <strong>and</strong> allow the assessment <strong>of</strong> the potential<br />

environmental impacts. It is at this stage that mitigation (e.g. re-routing) may<br />

be considered should the environmental impacts be significant. The completion<br />

<strong>of</strong> an appropriate level <strong>of</strong> site investigation in the early stages <strong>of</strong> the project<br />

will reduce the risks <strong>of</strong> delays during the consenting process <strong>and</strong> the risk <strong>of</strong><br />

major changes in the later stages <strong>of</strong> a project. It will also allow a more strategic<br />

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