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16.8 This effect could also be derived from a plan with policies whose detail remains largely<br />

unspecified in terms of quanta and locations of development, but also unspecified in terms of<br />

what development could do to fur<strong>the</strong>r <strong>the</strong> principles of sustainable development or <strong>the</strong><br />

enhancement and protection of vulnerable environmental receptors. This is highlighted by<br />

<strong>the</strong> contrast policies promoting growth like LP08 re‐development of DERA are considerably<br />

more beneficial across a greater number of sustainable objectives reflecting <strong>the</strong> positive<br />

impact in economic and social terms that generally accompany large scale redevelopment<br />

opportunities and generally do not per<strong>for</strong>m as well in SEA assessments.<br />

SEA Environmental Receptor Conclusion<br />

16.9 As outlined in Figure 6 in Section 3 above, <strong>the</strong> assessment framework used on this <strong>Local</strong> <strong>Plan</strong><br />

involves carrying out a number of different assessments/appraisals at any of <strong>the</strong> six levels<br />

identified in this flow diagram. It must be stressed that whilst <strong>the</strong>se are individual assessment<br />

in <strong>the</strong>ir own right – <strong>the</strong>y are ultimately integrated into <strong>the</strong> whole overall SAR process. For<br />

example Level 6 (HRA) was required to be completed, prior to Level 4 (SEA) and likewise Level<br />

3 (SA). This integrated method ensures that <strong>the</strong> SEA efficiently and effectively takes into<br />

account likely significant effects <strong>the</strong> <strong>Local</strong> <strong>Plan</strong> will have on <strong>for</strong> example <strong>the</strong> ER01 – Natural<br />

Environment and Biodiversity. The SA and SEA are thus fully in<strong>for</strong>med by an assessment of<br />

<strong>the</strong> most sensitive European Sites of TBH SPA and TAP&C SAC; an appropriate assessment at<br />

Level 6 and attached at Appendices 8 and 9.<br />

16.10 Overall, across <strong>the</strong> 10 environmental receptors identified in Table 1, a total of 1,230<br />

individual Level 4 SEA assessments were carried out on <strong>the</strong> combined 18 accepted policies<br />

and <strong>the</strong> 23 reasonable alternatives within this <strong>Local</strong> <strong>Plan</strong>. The results of this considerable<br />

ef<strong>for</strong>t on <strong>the</strong> part of <strong>the</strong> assessment team are contained within Appendix 2 and presented in<br />

Appendix 4.<br />

16.11 Whilst <strong>the</strong>se assessments provide ‘a general insight in terms of potential effects’, it is at<br />

varying degrees of usability. Generally, greater confidence can be placed on assessments that<br />

are closest to particular impact pathway, and correlates in <strong>the</strong> main to accepted industry<br />

practice. It follows that by combining results in a <strong>for</strong>m of summary, <strong>the</strong> resulting score needs<br />

to be considered with this conclusion caveat and thus can only be an indication of <strong>the</strong> likely<br />

effect implementation of <strong>the</strong> <strong>Local</strong> <strong>Plan</strong> might have on <strong>the</strong> environment as a whole. This is<br />

not to say that inferences cannot be drawn from <strong>the</strong> overall summary; on <strong>the</strong> contrary <strong>the</strong>re<br />

would be little point in carrying out an extensive exercise such as this if one could not. It is<br />

possible <strong>for</strong> <strong>the</strong> summaries to provide an indication of <strong>the</strong> possible ramifications <strong>the</strong> <strong>Local</strong><br />

<strong>Plan</strong> could have on a particular environmental receptor and/or overall environment.<br />

16.12 This lack of certainty is in markedly contrasted in terms of <strong>the</strong> conclusions that can be drawn<br />

from <strong>the</strong> Level 6 HRA assessments. Only a conclusion of ‘no adverse affect on <strong>the</strong> integrity of<br />

<strong>the</strong> relevant European Site’ in <strong>the</strong>se assessments will permit <strong>the</strong> Council to be able to agree<br />

to continue with and adopt <strong>the</strong> <strong>Local</strong> <strong>Plan</strong>.<br />

16.13 With <strong>the</strong> above cautions in mind, it is concluded that overall polices within <strong>the</strong> <strong>Local</strong> <strong>Plan</strong> are<br />

likely to result in a neutral effect on <strong>the</strong> environment of Runnymede. This neutral effect is<br />

largely derived from <strong>the</strong> plan where its policies are those which lack detail in terms of quanta<br />

and locations of development and are apparitional in nature. There are a few exceptions to<br />

this conclusion. In <strong>the</strong> main <strong>the</strong> exceptions relate to land‐use policies: such as Policy LP01,<br />

LP02, LP04, LP05, and Policy LP08 re‐development of DERA. The green belt relaxation<br />

promoted by Policy LP05 – RHUL is also considered to result in an overall uncertain adverse<br />

affects on <strong>the</strong> environment. Once implemented, <strong>the</strong>se policies will result in <strong>the</strong> promotion of<br />

development towards environmentally constrained locations and thus <strong>the</strong> uncertainty. In<br />

contrast, environmentally constrained polices, Policy LP03 – Development in Addlestone<br />

Urban Area is considered to result in an overall neutral effect. These conclusions have been<br />

considered in detail by <strong>the</strong> <strong>Local</strong> <strong>Plan</strong> policy drafting team and were taken into account in <strong>the</strong><br />

selection of preferred policies and rejection of o<strong>the</strong>r alternatives where applicable. This<br />

consideration is detailed within Sections 4 to 15 above under <strong>the</strong> heading ‘Consideration of<br />

Policy and its Alternatives on ER01 to ER10’ and has again been summarised in <strong>the</strong><br />

paragraphs following <strong>the</strong> SA Conclusions.<br />

Page | 204 Runnymede BC FINAL <strong>Sustainability</strong> <strong>Appraisal</strong> <strong>Report</strong> – Feb 2013

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