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Measurements were obtained in close proximity to individual wind turbines (~40 to 50m) for their full range of operating conditions, with snap-shot measurements at various positions between wind turbines and at a number of ranges away from the wind farm (ranging from about 50 m to 31 km), at all four compass points. The noise radiated from the operational wind turbines was typically comparable to or below the background noise level, and it was only certain frequency components that could be attributed to the operational wind turbines. The measured levels at the Sheringham Shoal OWF are comparable to those reported previously in the literature, where the same literature suggests that the underwater noise resulting from operational wind turbines would not be expected to result in injury to marine mammals and fish. The resultant noise levels in proximity to the turbines are also substantially lower than those expected to result in the onset of a permanent threshold shift in hearing response (PTS), or even a temporary threshold shift in hearing response (TTS), in marine mammals (Southall et al., 2007). It is also unlikely that these noise levels would result in a behavioural response, except perhaps in very close proximity to the turbines and only for species which might be sensitive to the tonal frequencies radiated.</gco:CharacterString>
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            <gco:CharacterString>To meet the requirements of the licence condition, underwater acoustic measurements were performed at a number of locations within and outside the wind farm site including measurements adjacent to and between wind turbines, measurements within the wind farm site and measurements along transects away from the wind farm. This was achieved using a combination of mobile survey vessel (the Vidar) measurements and autonomous recorders:   a) Mobile survey vessel measurements were used to characterise underwater sound at various ranges and positions along transects radiating away from individual wind turbines (A1, A5 and K3), and from the wind farm site. The specific wind turbines measured were chosen based on the geology, penetration depth and water depth at the turbines, and the transects were chosen to capture variation in bathymetry in the area surrounding the wind farm. In addition to these survey vessel based transect measurements, underwater sound was also measured at a number of pseudo-random locations, between adjacent turbines within the wind farm site and also on the array boundary, to capture variability across the wind farm site. b) Autonomous recorders were used to characterise the sound radiated by two individual wind turbines under a range of environmental conditions (wind, sea state, tidal variations) over a period of 21 days (sufficient to capture the full operating range of the wind turbines). The autonomous recorders were moored around 4 m above the sea floor, about 50 m from turbines A1 and A5. These two deployment locations were chosen based on the variations in bathymetry and geology at the wind farm site. Consideration was also given to local shipping patterns (DECC, 2013) and wind farm 
operational requirements.</gco:CharacterString>
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        <gco:CharacterString>The Crown Estate</gco:CharacterString>
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                <gco:CharacterString>enquiries@thecrownestate.co.uk</gco:CharacterString>
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                <gco:CharacterString>EPSG Geodetic Parameter Registry</gco:CharacterString>
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              <gmd:date>
                <gmd:CI_Date>
                  <gmd:date>
                    <gco:Date>2022-11-29</gco:Date>
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