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8.32 An increase in population within Runnymede will increase demand <strong>for</strong> water resources which<br />

in turn will increase scarcity.<br />

Consideration of Policy and its Alternatives on ER04<br />

Policy LP01: Strategy <strong>for</strong> <strong>the</strong> Location of Development<br />

8.33 With regard to <strong>the</strong> SEA (Appendix 4) all policy options have an adverse impact on <strong>the</strong><br />

receptors. The implication is that any development is likely to have an impact on water<br />

resource and management due to <strong>the</strong> scale of development and <strong>the</strong> potential supply issues.<br />

The adverse impact on pathways WRM1 and 3 have regard to technical issues on water flow<br />

and water supply. However, this is a technical issue that can be resolved with <strong>the</strong> provision of<br />

investment in <strong>the</strong> infrastructure.<br />

8.34 The Level 6 HRA assessment has provided <strong>the</strong> Council with sufficient evidence <strong>for</strong> it to<br />

ascertain no adverse affect on <strong>the</strong> integrity of ei<strong>the</strong>r Thames Basin Heaths SPA or Thursley,<br />

Ash, Pirbright and Chobham SAC as a result of <strong>the</strong> implementation of <strong>the</strong> <strong>Local</strong> <strong>Plan</strong>. The<br />

Level 6 HRA <strong>Report</strong> is presented in Appendices 8 and 9.<br />

8.35 Having regard to <strong>the</strong> conclusion of SA in Appendix 3, overall, all <strong>the</strong> policy approaches have a<br />

mixed beneficial impact. It is noted that <strong>the</strong> impact on <strong>the</strong> air quality is adverse (RSF 16),<br />

whilst it also has a negative impact on <strong>the</strong> desire to conserve and enhance <strong>the</strong> region’s biodiversity<br />

(RSF 19).<br />

8.36 LP01 overall does not have a significantly different impact to <strong>the</strong> alternatives.<br />

Policy LP02: Housing Provision and Distribution<br />

8.37 With regard to <strong>the</strong> SEA (Appendix 4) alternatives LP02 and LP02‐A1 have a neutral impact.<br />

The remaining policy options have an adverse impact. It is not clear why <strong>the</strong> policy options<br />

vary in <strong>the</strong>ir impact but it is likely that <strong>the</strong> comprehensive approach that is offered by <strong>the</strong><br />

<strong>for</strong>mer DERA site addresses <strong>the</strong> key infrastructure issues. The assessment however clearly<br />

supports an option that is able to positively address <strong>the</strong> physical infrastructure issues.<br />

8.38 The Level 6 HRA assessment has provided <strong>the</strong> Council with sufficient evidence <strong>for</strong> it to<br />

ascertain no adverse affect on <strong>the</strong> integrity of ei<strong>the</strong>r Thames Basin Heaths SPA or Thursley,<br />

Ash, Pirbright and Chobham SAC as a result of <strong>the</strong> implementation of <strong>the</strong> <strong>Local</strong> <strong>Plan</strong>. The<br />

Level 6 HRA <strong>Report</strong> is presented in Appendices 8 and 9.<br />

8.39 Having regard to <strong>the</strong> conclusion of SA in Appendix 3, overall, all <strong>the</strong> policy approaches have a<br />

neutral impact. It is noted that <strong>the</strong> impact on RSF 14 (<strong>the</strong> reuse of urban land) is undermined<br />

by <strong>the</strong> green field alternatives, whilst <strong>the</strong> impact on air quality is adverse (RSF 16) <strong>for</strong> all<br />

alternatives. There is again an adverse impact on RSF 20 – <strong>the</strong> impact on <strong>the</strong> natural and<br />

heritage environment. The need to accommodate growth will have a consequence <strong>for</strong> all <strong>the</strong><br />

receptors, but <strong>the</strong> impact of <strong>the</strong> alternatives is not different <strong>for</strong> planned or unplanned<br />

growth.<br />

8.40 LP02 overall in <strong>the</strong> SA consideration does not have a different impact to <strong>the</strong> alternatives.<br />

They are all neutral.<br />

Policy LP03: Development in Addlestone Urban Area<br />

8.41 With regard to <strong>the</strong> SEA (Appendix 4) LP03 has a neutral impact, whilst LP03‐A1 and LP03‐A2<br />

have an adverse impact. When consideration is given to <strong>the</strong> affect on <strong>the</strong> pathways LP03‐A1<br />

and LP03‐A2 have an adverse impact on pathway WRM 1 – <strong>the</strong> flow of water and WRM 3 –<br />

<strong>the</strong> demand <strong>for</strong> water. These issues are not present with <strong>the</strong> alternative A reflecting <strong>the</strong><br />

proposed modest planned approach to development in <strong>the</strong> town. The reactive impact of<br />

LP03‐A1 and <strong>the</strong> larger impact of <strong>the</strong> significant development are less easy to quantify and<br />

manage.<br />

8.42 Having regard to <strong>the</strong> conclusion of SA in Appendix 3, overall, all <strong>the</strong> policy approaches have a<br />

neutral impact. The impact on air quality is uncertain/adverse (RSF 16) <strong>for</strong> all alternatives and<br />

this is reflected on <strong>the</strong> impact on <strong>the</strong> pathways. The need to accommodate growth will have a<br />

consequence <strong>for</strong> all <strong>the</strong> receptors, but <strong>the</strong> impact of <strong>the</strong> alternatives is not different <strong>for</strong><br />

planned or unplanned growth.<br />

Page | 115 Runnymede BC FINAL <strong>Sustainability</strong> <strong>Appraisal</strong> <strong>Report</strong> – Feb 2013

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