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BOC Immingham Dissolved Acetylene Project Environmental Statement: Vol. 2 Main Text<br />

18.28 The construction and operational assessment was undertaken for impacts on:<br />

� the qualifying interest features of the statutory designated Humber Estuary (incorporating all<br />

aspects of the qualifying features for the SSSI, SAC, SPA and Ramsar site) based on<br />

whether the qualifying features are likely to be within the zone of influence of the proposed<br />

development during construction and whether impacts could result in a significant effect; and<br />

� non-statutory designated sites, notable habitats and notable species together with the<br />

significance of effect on ecological receptors.<br />

18.29 The assessment of significance of impacts takes into account measures which have already been<br />

included within the Project to avoid or reduce ecological impacts. The assessment determined that<br />

the construction and operation of the Dissolved Acetylene Project would not result in adverse<br />

effects on the integrity of the SPA and Ramsar and that, although there could be negative impacts<br />

on ecological receptors, these would not be significant.<br />

18.30 The assessment concluded that the planned design, management and control of the Dissolved<br />

Acetylene Project in relation to ecology are sufficient; thus no specific mitigation measures have<br />

been identified. Nonetheless, several recommendations have been made (see Chapter 10) in<br />

relation to selection of piling methods, lighting design, planting landscaping, wildlife<br />

enhancements and the NEA.<br />

Noise and Vibration<br />

18.31 The assessment identified the following as the main potential sources of noise and vibration:<br />

� noise:<br />

- operation of fixed plant during construction and operation,<br />

- operation of mobile plant and general site activities during construction and operation,<br />

- increased traffic during construction and operation; and<br />

� vibration:<br />

- piling activities, and<br />

- HGV movements from increased traffic during construction and operation.<br />

18.32 The noise assessment focuses on impacts to human receptors; however, data from the noise<br />

assessment has been used to determine effects on ecological receptors (see Chapter 10 and the<br />

previous sub-Section of this Chapter).<br />

18.33 The noise assessment determined that:<br />

� on the basis of highly conservative, worst case assumptions the total noise levels (ambient<br />

noise and construction noise combined) have been predicted, at worst, to be no more than<br />

5 dBA higher than ambient noise levels. Considering the temporary nature of construction<br />

activities, this is considered an acceptable level of impact when assessed in accordance with<br />

BS 5228;<br />

� an appropriate noise target (44 dB (LAeq,T)) has been set at the nearest human noise sensitive<br />

receptor (Poplar Farm) in relation to operational noise;<br />

� combining the expected site operational noise levels with the existing ambient noise level at<br />

Poplar Farm, results in a noise level change of less than 1 dBA. In accordance with BS 4142,<br />

the assessment suggests that there is a positive indication that complaints are unlikely. Thus<br />

noise impacts associated with this noise level change are therefore expected to be negligible;<br />

� traffic noise impacts during construction and operation are expected to be negligible; and<br />

� no adverse vibration impacts are expected at nearby properties during the construction or<br />

operation of the proposed facility.<br />

5100935.404 Environmental Statement August 2011 303

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