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DRAFT Sustainability Appraisal Report for the Emerging Local Plan ...

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9.56 With regard to SA, overall, <strong>the</strong> preferred policy has a mixed effect on SA objectives, and <strong>the</strong><br />

alternatives both have a neutral effect. RSF 16 (to reduce air pollution and ensure continued<br />

air quality improvement) scores an uncertain effect <strong>for</strong> <strong>the</strong> preferred option while alternative<br />

1 has a neutral effect. Alternative 2 scores an adverse effect. For RSF 19 – to conserve and<br />

enhance <strong>the</strong> region’s biodiversity – LP05 has an adverse effect and LP05‐A2 a significantly<br />

adverse effect. LP05‐A1 again has a neutral effect. For both <strong>the</strong>se objectives LP05‐A1 scores<br />

better than LP05 but again <strong>the</strong>se are environmentally based objectives and do not take<br />

account of <strong>the</strong> social and economic benefits of <strong>the</strong> preferred policy option. Mitigating<br />

measures can be taken to enable any development of <strong>the</strong> site meet <strong>the</strong>se environmental<br />

objectives.<br />

Policy LP06: Development in Chertsey Urban Area<br />

9.57 With regard to SEA receptor ER05, <strong>the</strong> overall conclusion <strong>for</strong> LP06 is a neutral effect on <strong>the</strong><br />

receptor (See Appendix 4). This is because it has been judged that air quality is unlikely to be<br />

materially affected by <strong>the</strong> scale of development envisaged <strong>for</strong> <strong>the</strong> settlement area.<br />

9.58 The policy alternatives have a neutral and positive impact. The only uncertain impact relates<br />

to RSF 22 and RSF 23. However, this is probably has universal implications across all policies<br />

considered.<br />

Policy LP07: Development in Virginia Water<br />

9.59 The neutral impact of both policy options are noted with regard to <strong>the</strong> SEA (Appendix 4). The<br />

actual impact on <strong>the</strong> pathways is also neutral. The need to accommodate growth will have an<br />

impact on air quality but it is pleasing to note that it is neutral.<br />

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

neutral/positive impact. The need to accommodate growth will have a consequence <strong>for</strong> all<br />

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

growth.<br />

9.61 LP07 overall in <strong>the</strong> SA consideration does not have a different impact to <strong>the</strong> alternative, apart<br />

from being more positive.<br />

Policy LP08: The <strong>for</strong>mer DERA site, Longcross<br />

9.62 All <strong>the</strong> policy options have an adverse impact on <strong>the</strong> receptors (See Appendix 4). The affect<br />

of <strong>the</strong> policy options on <strong>the</strong> pathways addressing air quality is one of <strong>the</strong> three receptors that<br />

is particularly critical. In <strong>the</strong> round <strong>the</strong> alternatives have a adverse/significantly adverse affect<br />

on all <strong>the</strong> pathways, and it is noted that alternative LP08‐A2 has an adverse affect on<br />

receptorAQ1‐2.<br />

9.63 The assessments reflect <strong>the</strong> impact pathways AQ1 and AQ2, emissions to air associated with<br />

traffic on <strong>the</strong> roads in <strong>the</strong> borough, and emissions to air associated with<br />

construction/maintenance of <strong>the</strong> Borough’s infrastructure, including residential and<br />

commercial assets. Again <strong>the</strong>se scores are to be expected against <strong>the</strong> level of development<br />

proposed by each option.<br />

9.64 The third impact pathway, emissions to air associated with heating proposed residential and<br />

commercial property in Runnymede (AQ3), has an adverse impact effect <strong>for</strong> all policy options.<br />

This is because <strong>the</strong> consequences of new development are to generate requirements <strong>for</strong><br />

heating. However quantities or methods of heating are not known at this stage, but it can be<br />

expected that <strong>the</strong> consequences <strong>the</strong>se impacts are relatively predictable.<br />

9.65 Each of <strong>the</strong> policy options will impact on <strong>the</strong> receptors given <strong>the</strong> quantum of development.<br />

Some impact on <strong>the</strong> receptors differently depending on location, but <strong>the</strong> overall assessment<br />

does not give rise to a clear preferred policy approach.<br />

9.66 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 />

Page | 130 Runnymede BC FINAL <strong>Sustainability</strong> <strong>Appraisal</strong> <strong>Report</strong> – Feb 2013

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