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

Impact Assessment<br />

Construction<br />

7.73 The land contamination impact assessment is based on the change in risk between the baseline<br />

and the construction phase. Construction activities by their very nature (and as described earlier)<br />

slightly increase the likelihood of exposure to contamination introduce potential sources. Good<br />

practice methods will be employed which will include measures to minimise the pathway and or<br />

reduce the source potential for exposure. A CEMP will be prepared and implemented, which will<br />

ensure that appropriate procedures will be in place to minimise risks and provide a means of<br />

monitoring their effectiveness. In addition, a construction waste management plan (WMP) will be<br />

developed and implemented as part of the CEMP. On the basis of the above, the construction<br />

phase contamination risk assessment is summarised as follows:<br />

� on site human receptors: the probability of the PPL is considered ‘low likelihood’ and the<br />

consequence is considered ‘mild’. Construction activities could increase the potential for<br />

exposure to contaminants in soil (if these are present) and vapour ground gas because<br />

construction activities involve the handling of soil and have the potential to encounter<br />

groundwater by excavation dewatering (potential sources). However, good practice methods<br />

are implemented to reduce such exposure and the risk identified as ‘low’;<br />

� offsite human receptors: the probability of the PPL is considered ‘unlikely’ and the<br />

consequence is considered ‘mild’. Construction activities could increase the potential for<br />

exposure to contaminants in windblown, soil-derived dust (if contaminants are present) and<br />

migrating vapour ground gas because construction activities involve the handling of soil<br />

(potential sources) and potentially changing the vapour ground gas regime. However, good<br />

practice methods are implemented to reduce such exposure activities and the risk identified<br />

as ‘very low’;<br />

� controlled waters receptors (groundwater in the Superficial Deposits): the probability of the<br />

PPL is considered ‘low likelihood’ and the consequence is considered ‘mild’. Construction<br />

activities could increase the potential for mobilisation of contaminants, for example, increased<br />

infiltration and leaching, accidental spillage of pollutants, etc. but good practice methods are<br />

implemented to reduce this possibility and the risk identified as ‘low’;<br />

� controlled waters receptors (Humber Estuary): the probability of the PPL is considered ‘low<br />

likelihood’ and the consequence is considered ‘mild’. Construction activities could increase<br />

the potential for mobilisation of contaminants, for example, in surface water runoff, but good<br />

practice methods are implemented to reduce this possibility and the risk identified as ‘low’;<br />

� on site property receptors (crops): this PPL no longer exists as the on site crops will have<br />

been removed;<br />

� offsite property receptor (crops): the probability of the PPL is considered ‘unlikely’ and the<br />

consequence is considered ‘minor’. Construction activities could increase the potential for<br />

mobilisation of contaminants in windblown, soil-derived dust, but good practice methods are<br />

implemented to reduce this possibility and the risk identified as ‘very low’; and<br />

� offsite property receptor (buildings): the probability of the PPL is considered ‘unlikely’ and the<br />

consequence is considered ‘minor’. Construction activities could increase the potential for<br />

mobilisation of vapours ground gas but good practice methods are implemented to reduce<br />

this possibility and the risk identified as ‘very low’.<br />

7.74 Based on the above, the impact assessment is summarised in Table 7.3.<br />

5100935.404 Environmental Statement August 2011 107

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