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

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Evolution of Baseline condition in Absence of <strong>Plan</strong><br />

7.25 As Runnymede continues to experience pressure <strong>for</strong> fur<strong>the</strong>r development, impact on land,<br />

soil and mineral resources are inevitable. This may adversely affect land by changing its use<br />

from agriculture to urban and thus its usability <strong>for</strong> food production. Runnymede has no good<br />

quality agriculture land or soils, so it is unlikely that development approved in Runnymede<br />

will have a significant adverse affect on this receptor. On <strong>the</strong> o<strong>the</strong>r hand in terms of<br />

contaminated land, development can be <strong>the</strong> vehicle to initiate its clean‐up and restoration.<br />

Pressure to develop will inevitably increase <strong>the</strong> use of resources particularly mineral<br />

resources and thus increasing adverse effects on <strong>the</strong> environment that can result from<br />

extraction.<br />

7.26 It is unreasonable to think that all contaminated land within <strong>the</strong> borough will be eradicated or<br />

that large volumes of contaminated land will be gained, <strong>the</strong>re will <strong>the</strong>re<strong>for</strong>e be limited<br />

evolution of <strong>the</strong> baseline as only small pockets of contaminated land will be encountered and<br />

remediated.<br />

Potential Impact Pathways<br />

LSMR1 Reduction of land through development<br />

7.27 Pressure <strong>for</strong> development may increase <strong>the</strong> removal of land that is currently open to be<br />

developed <strong>for</strong> o<strong>the</strong>r purposes.<br />

LSMR2 Reduction of soil through development and potential contamination<br />

7.28 The pressure <strong>for</strong> development may require <strong>the</strong> removal of soil <strong>for</strong> development. If this is on<br />

land that has not been previously developed it may result in adverse impacts. In contrast<br />

<strong>the</strong>re is little high quality soil in <strong>the</strong> borough, and <strong>the</strong>re<strong>for</strong>e a reduction in agricultural<br />

opportunities is unlikely.<br />

LSMR3 Pressure to increase use of mineral resources<br />

7.29 The increased use of minerals resources increases damage to <strong>the</strong> local environment within<br />

Runnymede at extraction locations. It also has wider implications in <strong>the</strong> collection of <strong>the</strong>se<br />

resources <strong>for</strong> removal such as increased traffic contributing to a reduction in air quality as<br />

well as increasing number of areas needing reclamation.<br />

Consideration of Policy and its Alternatives on ER03<br />

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

7.30 With regard to <strong>the</strong> SEA (Appendix 4) <strong>the</strong> impact of <strong>the</strong> policy approaches is mixed and<br />

neutral. This does not give a definitive view on <strong>the</strong> preferred alternative. The effect on <strong>the</strong><br />

individual pathways does not highlight any particularly adverse impacts.<br />

7.31 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 />

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

Policy LP02: Housing Provision and Distribution<br />

7.33 With regard to <strong>the</strong> SEA <strong>the</strong> policy option LP02 is neutral; while <strong>the</strong> o<strong>the</strong>r policy options have<br />

an uncertain through to a significantly adverse impact. This impact is illustrated by <strong>the</strong> impact<br />

on <strong>the</strong> pathways where alternatives LP02‐A2(b), LP02‐A2(c) and LP02‐A3(a) have a particular<br />

impact on LSMR 1,2 and 3 uncertain However, this reflects <strong>the</strong> impact on land use, soil and<br />

<strong>the</strong> increase on resources arising from different scales of development. This assessment has<br />

implications <strong>for</strong> <strong>the</strong> alternatives LP02‐A2(b), LP02‐A2(c) and LP02‐A3(a) that have a<br />

particularly detrimental impact LP02 per<strong>for</strong>ms more positively and has less impact<br />

7.34 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 />

Page | 101 Runnymede BC FINAL <strong>Sustainability</strong> <strong>Appraisal</strong> <strong>Report</strong> – Feb 2013

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