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

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infrastructure such as motorways and roads to social facilities such as libraries.<br />

9.36 Bringing new retail and residential development into <strong>the</strong> town centres may require upgrading<br />

or expanding existing infrastructure networks. It is reasonable to expect <strong>the</strong>se commercial<br />

uses would require energy, which in turn will contribute cumulatively to adverse air quality<br />

within Runnymede.<br />

AQ3 Emissions to air associated with heating and resulting from <strong>the</strong> proposed residential and<br />

commercial property in Runnymede.<br />

9.37 An increase in residential and commercial development will increase <strong>the</strong> amount of energy<br />

usage which will in turn decrease air quality. Whilst it may be argued that new stock will be<br />

more likely to be energy efficient in relation to older housing and commercial stock, increased<br />

stock will still contribute to energy usage and in turn adverse air quality.<br />

Consideration of Policy and its Alternatives on ER05<br />

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

9.38 With regard to <strong>the</strong> SEA (Appendix 4) LP01 has an uncertain impact on ER05, but LP01‐A1 and<br />

LP01‐A2 have an adverse impact on <strong>the</strong> receptor. Within <strong>the</strong> pathways LP01 and LP01‐A1<br />

have an adverse impact on pathway AQ1‐2, but LP01 has a neutral impact on AQ3. Marginally<br />

LP01 has a lesser impact than <strong>the</strong> o<strong>the</strong>r alternatives. In <strong>the</strong> round <strong>the</strong> scale of development<br />

proposed will by its very nature have a negative effect. In general LP01 has a lesser impact<br />

than <strong>the</strong> o<strong>the</strong>r alternatives. (See Appendix 4).<br />

9.39 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 />

9.40 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 />

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

Policy LP02: Housing Provision and Distribution<br />

9.42 With regard to <strong>the</strong> SEA (Appendix 4) <strong>the</strong> impact of all policy options on air quality is <strong>for</strong> <strong>the</strong><br />

most part uncertain or adverse. However, it is noted that alternatives LP02‐A3 (a) and LP02‐<br />

A3(b) have a significantly adverse impact that should be an important factor when<br />

considering <strong>the</strong> alternatives. The impact on <strong>the</strong> pathways is particularly noted <strong>for</strong> <strong>the</strong> LP02<br />

A3(a) and LP02 –A3(B) alternatives – this reflects <strong>the</strong> larger quantum of development. It is<br />

particularly noted that <strong>the</strong> LP02 A3(a) and LP02 A3(b) alternatives have significantly adverse<br />

effect on pathways AQ1‐3 – Whilst LP02 has an adverse impact on AQ3 (emissions to air<br />

resulting from new development) (See Appendix 4). It is inevitable that additional<br />

development will give rise to an impact on air quality – this can not be avoided, but can be<br />

better managed by a planned approach.<br />

9.43 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 />

9.44 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 />

Page | 128 Runnymede BC FINAL <strong>Sustainability</strong> <strong>Appraisal</strong> <strong>Report</strong> – Feb 2013

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