M1 JUNCTION 19 IMPROVEMENT ENVIRONMENTAL STATEMENT VOLUME 2 CHAPTER 9 – ROAD DRAINAGE AND THE WATER ENVIRONMENT Page Not Used B0531000_ID_70-EIA Vol 2 Chap 9 <strong>Road</strong> Drainage <strong>and</strong> <strong>the</strong> Water Environment Final Rev 4.doc Page 46
M1 JUNCTION 19 IMPROVEMENT ENVIRONMENTAL STATEMENT VOLUME 2 CHAPTER 9 – ROAD DRAINAGE AND THE WATER ENVIRONMENT 9.9 SUMMARY 9.9.1 An assessment of <strong>the</strong> effects of <strong>the</strong> proposed junction improvement, in relation to surface <strong>water</strong>, ground<strong>water</strong> <strong>and</strong> flood risk, has been undertaken following DMRB methodology, specifically developed for <strong>the</strong> assessment of <strong>the</strong> impacts of highway schemes, <strong>and</strong> based on advice from <strong>the</strong> EA. Impacts for <strong>the</strong> Catthorpe Viaduct have been indicated separately <strong>and</strong> included in combination with an overall assessment of <strong>the</strong> junction improvement. 9.9.2 Baseline conditions have been reviewed. The site is underlain by a mixture of non-aquifer <strong>and</strong> minor aquifers. The distribution of <strong>the</strong> latter are associated with <strong>the</strong> location of <strong>the</strong> various surface <strong>water</strong>courses. The site lies within <strong>the</strong> catchment of <strong>the</strong> River Avon, a main river, <strong>and</strong> <strong>the</strong> highway crosses <strong>the</strong> River Avon at a number of locations. There is one o<strong>the</strong>r main river, <strong>the</strong> Clay Coton Yelvertoft Brook. There are numerous o<strong>the</strong>r ordinary <strong>water</strong>courses / <strong>drainage</strong> ditches <strong>and</strong> ponds. 9.9.3 There are some ground<strong>water</strong> abstractions, including private potable supply, located within 1km of <strong>the</strong> highway, presumed to be sourced from <strong>the</strong> minor aquifer. There are no surface <strong>water</strong> abstractions, although <strong>the</strong>re is an important public <strong>water</strong> supply abstraction some seven kilometres downstream on <strong>the</strong> River Avon. 9.9.4 The main rivers are of good <strong>water</strong> quality. However, <strong>the</strong> existing highway <strong>drainage</strong> undergoes little treatment prior to discharge <strong>and</strong>, in addition, <strong>the</strong>se receiving <strong>water</strong>courses are very vulnerable to pollution incidents. 9.9.5 Without mitigation, construction work has <strong>the</strong> potential to adversely impact <strong>the</strong> <strong>water</strong> <strong>environment</strong>. The main potential impact is pollution of surface <strong>water</strong>s. It is assumed that good site practice as incorporated within <strong>and</strong> fundamental to <strong>the</strong> CEMP would be followed during <strong>the</strong> construction phase. The overall assessment score for <strong>the</strong> construction phase is of a Moderate Adverse effect – however, this is considered to be conservative as it reflects <strong>the</strong> inclusion of potential pollution of <strong>the</strong> River Avon drinking <strong>water</strong> supply. This would be a temporary risk, <strong>and</strong> of very short potential duration as <strong>the</strong> treatment ponds would be constructed early, providing mitigation for accidental spillage. 9.9.6 For <strong>the</strong> proposed junction improvement, <strong>the</strong> <strong>drainage</strong> scheme for <strong>the</strong> highway operation would upgrade <strong>the</strong> existing arrangements with spillage containment, <strong>water</strong> treatment <strong>and</strong> attenuation where required. It is assumed that maintenance <strong>and</strong> management of <strong>the</strong> operational scheme would be undertaken as necessary. The overall assessment score for <strong>the</strong> operational phase is of a Slight Beneficial effect. 9.9.7 With respect to ground<strong>water</strong>, <strong>the</strong>re is a potential for construction of cuttings to lead to a lowering of <strong>the</strong> <strong>water</strong> table within <strong>the</strong> minor aquifer. However, this effect would be localised <strong>and</strong> of Neutral significance. O<strong>the</strong>r impacts on ground<strong>water</strong> are relatively insignificant, <strong>and</strong> few mitigation measures are proposed or required. This results in <strong>the</strong> residual impact being little changed from <strong>the</strong> current situation. 9.9.8 In terms of flood risk, <strong>the</strong> widening of <strong>the</strong> A14 embankments <strong>and</strong> <strong>the</strong> creation of two bridleway bridges would reduce <strong>the</strong> storage capacity in <strong>the</strong> River Avon floodplain. However, flood compensation would be provided <strong>and</strong> so <strong>the</strong>re would be no net loss of flood storage. Attenuation ponds would reduce <strong>the</strong> discharge rate for highway runoff across <strong>the</strong> scheme by at least 20%, <strong>and</strong> would <strong>the</strong>refore have a Slight Beneficial effect on flood risk. 9.9.9 The junction improvement would satisfy <strong>the</strong> requirements of DMRB for routine runoff <strong>and</strong> pollution incidents from accidental spillages. Details of <strong>the</strong> DMRB calculations are included in Appendix A. B0531000_ID_70-EIA Vol 2 Chap 9 <strong>Road</strong> Drainage <strong>and</strong> <strong>the</strong> Water Environment Final Rev 4.doc Page 47